Mercury is the metal to check in fish, and species is the main driver: mean total mercury in European data ran from about 33 µg/kg in salmon and trout to 1,212 µg/kg in swordfish.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source →2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
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Metals of concern:
Methylmercury in large predatory fish; lead and cadmium are usually low in monitored fish, and most arsenic is organic.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source →3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →4Dietary exposure to inorganic arsenic in the European populationEFSA Journal 2014;12(3):3597Read source →
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Main drivers:
Species, size and age, farmed or wild origin, and polluted waters for cadmium and lead.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source →5Assessing mercury exposure to water and fish of the Mackenzie watershed using a Bayesian network analysisIntegrated Environmental Assessment and ManagementRead source →6PCBs and Heavy Metals in Farmed, Escaped and WildPeer-reviewed articleRead source →7Heavy Metal Levels and Cancer Risk Assessments of the Commercial Denis, Sparus aurata Collected from Bardawil Lake and Private Fish Farm Waters as a Cultured Source, EgyptNot reportedRead source →
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Practical framing:
Choose lower-mercury species and ask for wet-weight lot results naming total mercury or methylmercury.8Advice About Eating Fish — For Those Who Might Become or Are Pregnant or Breastfeeding and Children Ages 1 to 11 YearsU.S. FDA and U.S. EPARead source →9Report of the 17th Session of the Codex Committee on Contaminants in Foods (REP24/CF17)Joint FAO/WHO Food Standards Programme, Codex Alimentarius CommissionRead source →
Fish overview
Mercury decides most questions about fish, and the species on the plate matters far more than anything else that has been measured. Across European monitoring results compiled by EFSA, mean total mercury in fish muscle ran from about 31–35 µg/kg in salmon and trout and 32–44 µg/kg in sardine, through 91–96 µg/kg in cod and whiting and 286–291 µg/kg in tuna, to 688–695 µg/kg in shark and 1,210–1,214 µg/kg in swordfish (lower- to upper-bound means, wet weight).1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source → WHO GEMS/Food submissions from Europe show the same order, with a median of about 184 µg/kg for tuna against 80 µg/kg for cod and 18–30 µg/kg for sardine.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
Most of the mercury in fish muscle is methylmercury, the form that drives intake limits. In 210 retail fish samples from Japan, methylmercury made up about 60–90% of total mercury once total mercury was at least 100 µg/kg, close enough that total mercury is used as a screening measure.10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source → The EU sets 500 µg/kg of total mercury for most fish muscle and 1,000 µg/kg for large predators such as tuna, swordfish and shark, while Codex sets methylmercury levels of 1,200 µg/kg for tuna and 1,600 µg/kg for shark.9Report of the 17th Session of the Codex Committee on Contaminants in Foods (REP24/CF17)Joint FAO/WHO Food Standards Programme, Codex Alimentarius CommissionRead source →11Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006Official Journal of the European UnionRead source →
Lead and cadmium are usually low in fish muscle where monitoring is routine, and arsenic in fish is mostly in organic forms. US Total Diet Study composites of baked cod, salmon and tilapia had lead below 4 µg/kg and cadmium at or below about 1 µg/kg, and EFSA’s European fish muscle data gave a cadmium median of 5 µg/kg.3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →12Scientific Opinion of the Panel on Contaminants in the Food Chain on a request from the European Commission on cadmium in foodThe EFSA JournalRead source → Total arsenic in marine fish is often in the thousands of µg/kg, such as 4,500 µg/kg in US baked cod, but inorganic arsenic averaged only 0.7–20 µg/kg (lower bound) across European fish species.3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →4Dietary exposure to inorganic arsenic in the European populationEFSA Journal 2014;12(3):3597Read source →
Higher lead and cadmium values come mostly from small surveys of rivers, lagoons and coasts near mining, industry or wastewater, and many of the most extreme ones fail checks against their own papers.13Hazardous effects of heavy metal pollution on Nile tilapia in the aquatic ecosystem of the Eastern Delta in EgyptBMC Veterinary ResearchRead source →14Health Risk Assessment of Heavy Metals in Marine Fish Caught from the Northwest Persian GulfBiological Trace Element ResearchRead source →15ICP-MS-based quantitative analysis and risk assessment of metal(loid)s in fish species from Chennai, IndiaFrontiers in Public HealthRead source → For a buyer or a regular eater, the supported priorities are species and size choice for mercury, verified lot results for the analyte that applies to the species, and keeping total and inorganic arsenic apart.8Advice About Eating Fish — For Those Who Might Become or Are Pregnant or Breastfeeding and Children Ages 1 to 11 YearsU.S. FDA and U.S. EPARead source →11Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006Official Journal of the European UnionRead source →16Commission Regulation (EU) 2025/1891 of 17 September 2025 amending Regulation (EU) 2023/915 as regards maximum levels of inorganic arsenic in fish and other seafoodOfficial Journal of the European UnionRead source →
What counts as fish on this page
This page covers finfish eaten by people: the muscle, fillet or whole small fish of marine, freshwater and farmed species, and the canned, smoked, dried, salted, fermented and processed products made from them.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →11Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006Official Journal of the European UnionRead source → Fish oils and fish-liver oils, fish sauce and fish products such as fingers, cakes and collagen supplements are kept as separate forms and never pooled with flesh.17Mercury Content in Fish Oil Food Supplements and Associated Health RiskProceedings 2023, 91, 364 (MDPI Proceedings — 14th European Nutrition Conference FENS 2023)Read source →18Mercury Exposure from the Consumption of Dietary Supplements Containing Vegetable, Cod Liver, and Shark Liver OilsInternational Journal of Environmental Research and Public HealthRead source →19Determination of Inorganic Arsenic in Seaweed and Seafood by LC-ICP-MS: Method ValidationJournal of AOAC InternationalRead source →
Shellfish, crustaceans, cephalopods, marine mammals, fish feed and fish offal are outside the scope, as are fish-containing infant foods, which have their own product page.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →20Chemical characterization of baby food consumed in ItalyPLOS ONERead source → Categories that mix finfish with shellfish, common in total diet studies and some European summaries, are also excluded because their results cannot be attributed to fish.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →21Assessment of the dietary exposure to arsenic, cadmium, lead and mercury of the population of the EU Member StatesReports on tasks for scientific cooperation, SCOOP Task 3.2.11Read source →
Measurements are kept in the basis the source reports: wet weight (as sold or eaten), dry weight, or basis not stated; dry-weight results are not converted without the paper’s own moisture data.6PCBs and Heavy Metals in Farmed, Escaped and WildPeer-reviewed articleRead source →7Heavy Metal Levels and Cancer Risk Assessments of the Commercial Denis, Sparus aurata Collected from Bardawil Lake and Private Fish Farm Waters as a Cultured Source, EgyptNot reportedRead source → Total mercury, methylmercury and mercury of unstated form are separate analytes, as are total, inorganic and organic arsenic species.4Dietary exposure to inorganic arsenic in the European populationEFSA Journal 2014;12(3):3597Read source →10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source →22Determination of Total Inorganic Arsenic in Fish, Shellfish and Fish ProductsAnalystRead source →
Heavy metal contamination profile of fish
The table holds every finfish result extracted from about 250 monitoring datasets, total diet studies and surveys: one row for each statistic a source reports for a species group, form, site and metal, so a mean, a median and a range from the same fish appear as separate rows.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source →2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →12Scientific Opinion of the Panel on Contaminants in the Food Chain on a request from the European Commission on cadmium in foodThe EFSA JournalRead source → Ratings place a reported mean, median or sample value against an HMI reference built only from the same species group, preparation form, analyte and basis; non-detects remain intervals and are never read as zero.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source → Rows that failed a check against their own paper stay visible with the specific reason and are not compared.13Hazardous effects of heavy metal pollution on Nile tilapia in the aquatic ecosystem of the Eastern Delta in EgyptBMC Veterinary ResearchRead source →14Health Risk Assessment of Heavy Metals in Marine Fish Caught from the Northwest Persian GulfBiological Trace Element ResearchRead source →15ICP-MS-based quantitative analysis and risk assessment of metal(loid)s in fish species from Chennai, IndiaFrontiers in Public HealthRead source →
Comparison methods and scope
Each row is one statistic a source reports for one fish subgroup and metal; a mean, median and range from the same fish are separate rows. Species groups, preparation forms (fresh, cooked, canned, smoked or dried, oil, products), mercury and arsenic species, and wet versus dry weight are never pooled. Ratings place a reported mean, median or sample result against an HMI reference built only from the same species group, form, analyte and basis. Same-study contrasts compare farmed with wild fish, a prepared form with fresh fish, or a subgroup with the study total. Held rows failed a check against their own paper and are shown but not compared.
First displayed analyte: Total mercury: 2885 findings from 153 sources. Each row retains its statistic and measurement basis.
Filter findings
7164 of 7164 findings · 19 analytes
About this table
| Food form | Collection scope | Finding | Comparison | Evidence |
|---|---|---|---|---|
188 findings · 27 studies · 61 spread figures folded in | ||||
| Tuna · cannedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador2022–2023 | range. | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | mean.Same samples: 40–370 µg/kg (range) | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | range. | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | mean.Same samples: 20–370 µg/kg (range) | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | range. | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | mean.Same samples: 20–370 µg/kg (range) | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | range. | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | mean.Same samples: 120–1,980 µg/kg (range) | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | range. | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | mean.Same samples: 120–1,980 µg/kg (range) | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | range. | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | mean.Same samples: 200–1,000 µg/kg (range) | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | range. | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | mean.Same samples: 60–780 µg/kg (range) | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | range. | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | mean.Same samples: 40–780 µg/kg (range) | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | range. | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | mean.Same samples: 40–690 µg/kg (range) | ||
| Tuna · cannedAguilar-Miranda et al. 2024 | Ecuador; fishing area not stated2022–2023 | range. | ||
| Tuna · cannedAl-Sulaiti et al. 2023 | Imported, origin not stated2021–2022dry weight | mean.Same samples: 15–255 µg/kg (range) | ||
| Tuna · cannedAl-Sulaiti et al. 2023 | Imported, origin not stated2021–2022 | mean. | ||
| Tuna · cannedAl-Sulaiti et al. 2023 | Imported, origin not stated2021–2022 | range. | ||
| Tuna · cannedBlanco et al. 2023 | various2011–2017basis not stated | mean.Same samples: 10–1,020 µg/kg (range) | ||
| Tuna · cannedBlanco et al. 2023 | various2011–2017basis not stated | median. | ||
| Tuna · cannedBlanco et al. 2023 | various2011–2017basis not stated | range. | ||
| Tuna · cannedDjedjibegovic et al. 2020 | Thailand2019 | mean.Same samples: 37–116 µg/kg (range) | ||
| Tuna · cannedDjedjibegovic et al. 2020 | Thailand2019 | range. | ||
| Tuna · cannedEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: up to 480 µg/kg (range maximum) | ||
| Tuna · cannedEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Tuna · cannedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Tuna · cannedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 10–290 µg/kg (range) | ||
| Tuna · cannedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Tuna · cannedFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Tuna · cannedFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Tuna · cannedFood 2019 | Retail/takeaway purchases across2013–2014 | mean. | ||
| Tuna · cannedGerman 2024 | Germany2012–2021basis not stated | mean.Same samples: 480 µg/kg (maximum) | ||
| Tuna · cannedGerman 2024 | Germany2012–2021basis not stated | max. | ||
| Tuna · cannedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Tuna · cannedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Tuna · cannedGladys et al. 2026 | Central Market of Lima2023 | not detected. | ||
| Tuna · cannedGladys et al. 2026 | Central Market of Lima2023 | mean. | ||
| Tuna · cannedGladys et al. 2026 | Central Market of Lima2023 | median. | ||
| Tuna · cannedGladys et al. 2026 | Central Market of Lima2023 | range. | ||
| Tuna · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 44–402 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 51–460 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 116–148 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 120–162 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 104–248 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 116–251 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 185–273 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 98–460 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 132–402 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 165–214 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 44–103 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 51–137 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedOlmedo et al. 2013 | Spain2009–2010 | below LOD. | ||
| Tuna · cannedOlmedo et al. 2013 | Andalusia, Spain2009–2010 | below LOD. | ||
| Tuna · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | not stated2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean.Same samples: 21–1,490 µg/kg (range) | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | range. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | range. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | median.Same samples: 11.3–351 µg/kg (range) | ||
| Tuna · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | range. | ||
| Tuna · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | mean. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 150–650 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 130–540 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 110–670 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 110–1,170 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 230–840 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 5–320 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 30–210 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 60–280 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 5–1,170 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 190–2,680 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 80–1,280 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 60–380 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean.Same samples: 174–191 µg/kg (range) | ||
| Tuna · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | range. | ||
| Tuna · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean.Same samples: 48–63 µg/kg (range) | ||
| Tuna · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | range. | ||
| Tuna · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean. | ||
| Tuna · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean. | ||
| Tuna · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean. | ||
| Tuna · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean. | ||
| Tuna · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean. | ||
| Tuna · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean. | ||
| Tuna · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean. | ||
| Tuna · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean. | ||
| Tuna · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean. | ||
| Tuna · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean. | ||
| Tuna · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Holland; FAO area 672017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Iran2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Canada; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Seychelles2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Maldives2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Mauritius2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin The Ivory Coast2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Holland; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Spain2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Philippines2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Equator [Ecuador]2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin United Arab Emirates2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | developed countries2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | developing countries2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Algeria2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Argentina2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Brazil2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Equator [Ecuador]2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Morocco2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Portugal2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Indonesia2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Tunisia2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Spain; FAO area 512017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Indonesia2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Italy2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Turkey2017–2019 | mean. | ||
| Tuna · cannedValidation of… 2022 | Turkey2016–2017 | mean.Same samples: up to 220 µg/kg (range maximum) | ||
| Tuna · cannedValidation of… 2022 | Turkey2016–2017 | range. | ||
| Tuna · cannedValidation of… 2022 | Turkey2016–2017 | mean.Same samples: 80–510 µg/kg (range) | ||
| Tuna · cannedValidation of… 2022 | Turkey2016–2017 | range. | ||
| Tuna · cannedValidation of… 2022 | Turkey2016–2017 | mean.Same samples: 90–660 µg/kg (range) | ||
| Tuna · cannedValidation of… 2022 | Turkey2016–2017 | range. | ||
| Tuna · cannedValidation of… 2022 | Turkey2016–2017 | mean.Same samples: 40–530 µg/kg (range) | ||
| Tuna · cannedValidation of… 2022 | Turkey2016–2017 | range. | ||
| Tuna · cannedVariability of Mercury… 1990 | grocery stores2022basis not stated | mean.Same samples: 1,300 µg/kg (maximum) | ||
| Tuna · cannedVariability of Mercury… 1990 | grocery stores2022basis not stated | max. | ||
| Tuna · cannedVariability of Mercury… 1990 | grocery stores2022basis not stated | mean. | ||
| Tuna · cannedVoegborlo et al. 1999 | caught by commercial vessels offCollection date unreported | mean.Same samples: 200–660 µg/kg (range) | ||
| Tuna · cannedVoegborlo et al. 1999 | caught by commercial vessels offCollection date unreported | range. | ||
| Mackerel · cannedDjedjibegovic et al. 2020 | Morocco2019 | mean.Same samples: 42–624 µg/kg (range) | ||
| Mackerel · cannedDjedjibegovic et al. 2020 | Morocco2019 | range. | ||
| Mackerel · cannedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Mackerel · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Mackerel · cannedNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 12–23 µg/kg (range) | ||
| Mackerel · cannedNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Mackerel · cannedNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 19–23 µg/kg (range) | ||
| Mackerel · cannedNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Mackerel · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Mackerel · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | mean.Same samples: 1.7–90.5 µg/kg (range) | ||
| Mackerel · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | range. | ||
| Horse mackerel, jacks and trevally · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean.Same samples: 50–61 µg/kg (range) | ||
| Horse mackerel, jacks and trevally · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | range. | ||
| Horse mackerel, jacks and trevally · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean. | ||
| Horse mackerel, jacks and trevally · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean. | ||
| Herring · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Herring · cannedPawlaczyk et al. 2020 | Atlantic2019–2020basis not stated | mean. | ||
| Herring · cannedPawlaczyk et al. 2020 | Baltic Sea2019–2020basis not stated | mean. | ||
| Herring · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | mean. | ||
| Herring · cannedVariability of Mercury… 1990 | grocery stores2022basis not stated | mean. | ||
| Sardine and pilchard · cannedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 40–70 µg/kg (range) | ||
| Sardine and pilchard · cannedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Sardine and pilchard · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Sardine and pilchard · cannedOlmedo et al. 2013 | Spain2009–2010 | below LOD. | ||
| Sardine and pilchard · cannedOlmedo et al. 2013 | Spain2009–2010 | below LOD. | ||
| Sardine and pilchard · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | mean. | ||
| Sprat · cannedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Sprat · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | mean. | ||
| Anchovy · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Salmon · cannedAl-Sulaiti et al. 2023 | Imported; 2 wild, 1 unknown2021–2022dry weight | mean.Same samples: 12–35 µg/kg (range) | ||
| Salmon · cannedAl-Sulaiti et al. 2023 | Imported; 2 wild, 1 unknown2021–2022 | mean. | ||
| Salmon · cannedAl-Sulaiti et al. 2023 | Imported; 2 wild, 1 unknown2021–2022 | range. | ||
| Salmon · cannedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Salmon · cannedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Salmon · cannedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 30–30 µg/kg (range) | ||
| Salmon · cannedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Salmon · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Salmon · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | mean. | ||
| Salmon · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean.Same samples: 20–70 µg/kg (range) | ||
| Salmon · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | range. | ||
| Salmon · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean. | ||
| Salmon · cannedShim et al. 2004 | local stores around Lafayette2003basis not stated | mean. | ||
| Cod · cannedPawlaczyk et al. 2020 | Atlantic2019–2020basis not stated | mean. | ||
| Cod · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | mean. | ||
| Pollock and saithe · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | mean. | ||
| Marine fish, species not stated · cannedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Marine fish, species not stated · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | mean. | ||
| Marine fish, species not stated · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | median. | ||
| Fish, species not stated · cannedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cannedDabeka et al. 2003 | Retail, Ottawa, Canada1998–2000 | sample value. | ||
| Fish, species not stated · cannedDabeka et al. 2003 | Retail, Whitehorse, Canada1998–2000 | sample value. | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 10–470 µg/kg (range) | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: up to 615 µg/kg (range maximum) | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 3–450 µg/kg (range) | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Portugal national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · cannedFood 2016 | Major retailers, Dublin, Ireland2012–2014 | range. | ||
| Fish, species not stated · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | median. | ||
| Fish, species not stated · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | median. | ||
| Fish, species not stated · cannedPawlaczyk et al. 2020 | local markets in Lodz, Poland2019–2020basis not stated | median. | ||
83 findings · 12 studies · 3 spread figures folded in | ||||
| Tuna · cookedFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Tuna · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Tuna · cookedVera et al. 2018 | AzoresCollection date unreported | mean. | ||
| Mackerel · cookedVera et al. 2018 | Atlantic OceanCollection date unreported | mean. | ||
| Horse mackerel, jacks and trevally · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Sardine and pilchard · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Sardine and pilchard · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Sardine and pilchard · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Shad, hilsa and other herrings · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Shad, hilsa and other herrings · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Shad, hilsa and other herrings · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Salmon · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Salmon · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Trout and char · cookedFechner et al. 2022 | prepacked: Turkey 172017–2019basis not stated | mean. | ||
| Trout and char · cookedFechner et al. 2022 | prepacked: Turkey 172017–2019basis not stated | mean. | ||
| Trout and char · cookedFechner et al. 2022 | prepacked: Turkey 172017–2019basis not stated | mean. | ||
| Trout and char · cookedFechner et al. 2022 | prepacked: Turkey 172017–2019basis not stated | mean. | ||
| Trout and char · cookedGerman 2024 | Germany, Eastern region2012–2021basis not stated | mean. | ||
| Trout and char · cookedGerman 2024 | Germany, Northern region2012–2021basis not stated | mean. | ||
| Trout and char · cookedGerman 2024 | Germany, Southern region2012–2021basis not stated | mean. | ||
| Trout and char · cookedGerman 2024 | Germany, Western region2012–2021basis not stated | mean. | ||
| Trout and char · cookedGroleau et al. 2025 | Nunavik, Quebec, CanadaCollection date unreported | range. | ||
| Trout and char · cookedGroleau et al. 2025 | Nunavik, Quebec, CanadaCollection date unreported | max. | ||
| Trout and char · cookedGroleau et al. 2025 | PuvirnituqCollection date unreported | min. | ||
| Trout and char · cookedGroleau et al. 2025 | PuvirnituqCollection date unreported | range. | ||
| Trout and char · cookedGroleau et al. 2025 | Nunavik, Quebec, CanadaCollection date unreported | max. | ||
| Cod · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Cod · cookedFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Cod · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | mean. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | median. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | mean. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | median. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | mean. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | median. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | mean. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | median. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | mean. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | median. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | mean. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | median. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | mean. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | median. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | mean. | ||
| Cod · cookedIodine and Mercury… 2020 | Barents Sea2015–2017 | median. | ||
| Pollock and saithe · cookedFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Pollock and saithe · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Hake · cookedProducts et al. 2019 | South African retail storesCollection date unreported | range. | ||
| Hake · cookedVera et al. 2018 | South AfricaCollection date unreported | mean. | ||
| Hake · cookedVera et al. 2018 | South AmericaCollection date unreported | mean. | ||
| Plaice, flounder, sole and turbot · cookedFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Plaice, flounder, sole and turbot · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Plaice, flounder, sole and turbot · cookedVera et al. 2018 | ChannelCollection date unreported | mean. | ||
| Plaice, flounder, sole and turbot · cookedVera et al. 2018 | Goro, ItalyCollection date unreported | mean. | ||
| Halibut · cookedFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Halibut · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Sea bream and porgies · cookedVera et al. 2018 | Farmed, ItalyCollection date unreported | mean. | ||
| Scorpionfish and rockfish · cookedFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Scorpionfish and rockfish · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Anglerfish and monkfish · cookedVera et al. 2018 | Atlantic OceanCollection date unreported | mean. | ||
| Eel · cookedFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Eel · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Other marine fish · cookedProducts et al. 2019 | South African retail storesCollection date unreported | range. | ||
| Other marine fish · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Tilapia · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Carp and other cyprinids · cookedGerman 2024 | Germany, Eastern region2012–2021basis not stated | mean. | ||
| Carp and other cyprinids · cookedGerman 2024 | Germany, Northern region2012–2021basis not stated | mean. | ||
| Carp and other cyprinids · cookedGerman 2024 | Germany, Southern region2012–2021basis not stated | mean. | ||
| Carp and other cyprinids · cookedGerman 2024 | Germany, Western region2012–2021basis not stated | mean. | ||
| Catfish · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | below LOD. | ||
| Marine fish, species not stated · cookedLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean.Same samples: up to 1,390 µg/kg (range maximum) | ||
| Marine fish, species not stated · cookedLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | range. | ||
| Marine fish, species not stated · cookedLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean.Same samples: 50–4,590 µg/kg (range) | ||
| Marine fish, species not stated · cookedLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | range. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cookedDabeka et al. 2003 | Retail, Ottawa, Canada1998–2000 | sample value. | ||
| Fish, species not stated · cookedDabeka et al. 2003 | Retail, Whitehorse, Canada1998–2000 | sample value. | ||
| Fish, species not stated · cookedDabeka et al. 2003 | Retail, Ottawa, Canada1998–2000 | sample value. | ||
| Fish, species not stated · cookedDabeka et al. 2003 | Retail, Whitehorse, Canada1998–2000 | sample value. | ||
| Fish, species not stated · cookedFood 2019 | Retail/takeaway purchases across2013–2014 | mean. | ||
| Fish, species not stated · cookedLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean.Same samples: up to 470 µg/kg (range maximum) | ||
| Fish, species not stated · cookedLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | range. | ||
| Fish, species not stated · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
69 findings · 15 studies · 21 spread figures folded in | ||||
| Tuna · fish productEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Tuna · fish productMaria et al. 2022 | University of Valencia canteensCollection date unreporteddry weight | sample value. | ||
| Tuna · fish productMaria et al. 2022 | University of Valencia canteensCollection date unreporteddry weight | sample value. | ||
| Herring · fish productGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Salmon · fish productEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Cod · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | not detected. | ||
| Cod · fish productEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 10–60 µg/kg (range) | ||
| Cod · fish productEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Cod · fish productGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Cod · fish productMaria et al. 2022 | University of Valencia canteensCollection date unreporteddry weight | sample value. | ||
| Cod · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Cod · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Cod · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Cod · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Haddock · fish productEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Pollock and saithe · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 15–16 µg/kg (range) | ||
| Pollock and saithe · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Pollock and saithe · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | sample value. | ||
| Pollock and saithe · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | sample value. | ||
| Tilapia · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | not detected. | ||
| Catfish · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | max. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 5–23 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 3–21 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 6–23 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 16–42 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 19–83 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 21–46 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 10–33 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 19–27 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 22–44 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 5–26 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 4–22 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2004–2020 | median. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2004–2018 | median. | ||
| Fish, species not stated · fish productFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productDabeka et al. 2003 | Retail, Whitehorse, Canada1998–2000 | sample value. | ||
| Fish, species not stated · fish productDietary Intake of Toxic… 2022 | retail market2016–2018basis not stated | mean. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 121 µg/kg (maximum) | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 622 µg/kg (maximum) | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: up to 50 µg/kg (range maximum) | ||
| Fish, species not stated · fish productEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–30 µg/kg (range) | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–170 µg/kg (range) | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | mean.Same samples: 6–25 µg/kg (range) | ||
| Fish, species not stated · fish productEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | range. | ||
| Fish, species not stated · fish productFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Fish, species not stated · fish productFood 2011 | Australian state/territory2008 | median. | ||
| Fish, species not stated · fish productFood 2019 | Retail/takeaway purchases across2013–2014 | mean. | ||
| Fish, species not stated · fish productGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Fish, species not stated · fish productGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 9–22 µg/kg (range) | ||
| Fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 14–25 µg/kg (range) | ||
| Fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Fish, species not stated · fish productProducts et al. 2019 | South African retail storesCollection date unreported | range. | ||
| Fish, species not stated · fish productProducts et al. 2019 | South African retail storesCollection date unreported | mean. | ||
| Fish, species not stated · fish productProducts et al. 2019 | South African retail storesCollection date unreported | mean. | ||
| Fish, species not stated · fish productProducts et al. 2019 | South African retail storesCollection date unreported | mean. | ||
| Fish, species not stated · fish productProducts et al. 2019 | South African retail storesCollection date unreported | mean. | ||
| Fish, species not stated · fish productProducts et al. 2019 | South African retail storesCollection date unreported | mean. | ||
1,899 findings · 124 studies · 486 spread figures folded in | ||||
| Tuna · fresh or rawWHO GEMS/Food | WHO region EURO2004–2020 | median. | ||
| Tuna · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | mean.Same samples: 20–1,380 µg/kg (range) | ||
| Tuna · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | range. | ||
| Tuna · fresh or rawAl-Sulaiti et al. 2023 | Local, wild2021–2022dry weight | mean.Same samples: 32–52 µg/kg (range) | ||
| Tuna · fresh or rawAl-Sulaiti et al. 2023 | Local, wild2021–2022 | mean. | ||
| Tuna · fresh or rawAl-Sulaiti et al. 2023 | Local, wild2021–2022 | range. | ||
| Tuna · fresh or rawAl-Sulaiti et al. 2023 | Imported, country not stated2021–2022dry weight | mean.Same samples: 16–20 µg/kg (range) | ||
| Tuna · fresh or rawAl-Sulaiti et al. 2023 | Imported, country not stated2021–2022 | mean. | ||
| Tuna · fresh or rawAl-Sulaiti et al. 2023 | Imported, country not stated2021–2022 | range. | ||
| Tuna · fresh or rawAl-Sulaiti et al. 2023 | Local and imported combined2021–2022dry weight | mean.Same samples: 16–52 µg/kg (range) | ||
| Tuna · fresh or rawAl-Sulaiti et al. 2023 | Local and imported combined2021–2022 | mean. | ||
| Tuna · fresh or rawAl-Sulaiti et al. 2023 | Local and imported combined2021–2022 | range. | ||
| Tuna · fresh or rawAnura et al. 2022 | Indian Ocean offshore pelagicCollection date unreported | mean.Same samples: 20–430 µg/kg (range) | ||
| Tuna · fresh or rawAnura et al. 2022 | Indian Ocean offshore pelagicCollection date unreported | range. | ||
| Tuna · fresh or rawBluefin Tuna (Thunnus… 2019 | Caught by purse seine on2015–2017 | mean. | ||
| Tuna · fresh or rawBluefin Tuna (Thunnus… 2019 | Caught by purse seine on2015–2017 | mean. | ||
| Tuna · fresh or rawBluefin Tuna (Thunnus… 2019 | Caught by purse seine on2015–2017 | mean. | ||
| Tuna · fresh or rawBluefin Tuna (Thunnus… 2019 | Caught by traps at Carloforte2015–2017 | mean. | ||
| Tuna · fresh or rawBluefin Tuna (Thunnus… 2019 | Caught by traps at Carloforte2015–2017 | mean. | ||
| Tuna · fresh or rawBluefin Tuna (Thunnus… 2019 | Caught by traps at Carloforte2015–2017 | mean. | ||
| Tuna · fresh or rawBrodziak-Dopierala et al. 2023 | FAO 342021–2022basis not stated | mean. | ||
| Tuna · fresh or rawBrodziak-Dopierala et al. 2023 | FAO 342021–2022basis not stated | max. | ||
| Tuna · fresh or rawBrodziak-Dopierala et al. 2023 | FAO 512021–2022basis not stated | mean. | ||
| Tuna · fresh or rawChristian et al. 2024 | Antigua and Barbuda2005–2023 | geometric mean.Same samples: 10–680 µg/kg (range) | ||
| Tuna · fresh or rawChristian et al. 2024 | Antigua and Barbuda2005–2023 | range. | ||
| Tuna · fresh or rawDjedjibegovic et al. 2020 | Portugal2019 | mean.Same samples: 114–309 µg/kg (range) | ||
| Tuna · fresh or rawDjedjibegovic et al. 2020 | Portugal2019 | range. | ||
| Tuna · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 3,370 µg/kg (maximum) | ||
| Tuna · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Tuna · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Tuna · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Tuna · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Tuna · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Tuna · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Tuna · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 60–550 µg/kg (range) | ||
| Tuna · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 36–178 µg/kg (range) | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 50–770 µg/kg (range) | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Tuna · fresh or rawEuropean et al. 2004 | Italy national submission to SCOOP1990–2002basis not stated | mean. | ||
| Tuna · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | mean.Same samples: 3,000 µg/kg (maximum) | ||
| Tuna · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | median. | ||
| Tuna · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | max. | ||
| Tuna · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | mean.Same samples: 1,500–3,000 µg/kg (range) | ||
| Tuna · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | range. | ||
| Tuna · fresh or rawGenevieve et al. 2023 | local supermarketCollection date unreportedbasis not stated | range. | ||
| Tuna · fresh or rawGerman 2024 | Germany2012–2021basis not stated | mean.Same samples: 690 µg/kg (maximum) | ||
| Tuna · fresh or rawGerman 2024 | Germany2012–2021basis not stated | max. | ||
| Tuna · fresh or rawHandayani et al. 2019 | southern Indian Ocean2012–2017basis not stated | mean. | ||
| Tuna · fresh or rawHandayani et al. 2019 | southern Indian Ocean2012–2017basis not stated | max. | ||
| Tuna · fresh or rawHandayani et al. 2019 | western Pacific Ocean2012–2017basis not stated | mean. | ||
| Tuna · fresh or rawHandayani et al. 2019 | western Pacific Ocean2012–2017basis not stated | max. | ||
| Tuna · fresh or rawHandayani et al. 2019 | southern Indian Ocean2012–2017basis not stated | mean. | ||
| Tuna · fresh or rawHandayani et al. 2019 | western Pacific Ocean2012–2017basis not stated | mean. | ||
| Tuna · fresh or rawHandayani et al. 2019 | western Pacific Ocean2012–2017basis not stated | max. | ||
| Tuna · fresh or rawLehel et al. 2023 | Sri LankaCollection date unreported | below LOD. | ||
| Tuna · fresh or rawLehel et al. 2023 | Sri LankaCollection date unreported | range. | ||
| Tuna · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Tuna · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Tuna · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Tuna · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Tuna · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Tuna · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Tuna · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Tuna · fresh or rawOktariani et al. 2023 | FAO Fishing Zone 572012–2016 | range. | ||
| Tuna · fresh or rawOktariani et al. 2023 | FAO Fishing Zone 712012–2016 | range. | ||
| Tuna · fresh or rawOlmedo et al. 2013 | Canary Islands, Spain2009–2010 | median. | ||
| Tuna · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Tuna · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 140–570 µg/kg (range) | ||
| Tuna · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Tuna · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Tuna · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Tuna · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Tuna · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Tuna · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Tuna · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Tuna · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Tuna · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Tuna · fresh or rawSimultaneous speciation… 2023 | Indian OceanCollection date unreported | mean. | ||
| Tuna · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Tuna · fresh or rawTotal mercury… 1982 | coast of Arraial do Cabo2018 | mean. | ||
| Tuna · fresh or rawTotal mercury… 1982 | coast of Arraial do Cabo2018 | mean. | ||
| Tuna · fresh or rawTotal mercury… 1982 | coast of Arraial do Cabo2018 | range. | ||
| Tuna · fresh or rawTotal mercury… 1982 | coast of Arraial do Cabo2018 | range. | ||
| Tuna · fresh or rawTotal mercury… 1982 | coast of Arraial do Cabo2018 | mean. | ||
| Tuna · fresh or rawTotal mercury… 1982 | coast of Arraial do Cabo2018 | range. | ||
| Tuna · fresh or rawTotal mercury… 1982 | coast of Arraial do Cabo2018 | range. | ||
| Tuna · fresh or rawVera et al. 2018 | AzoresCollection date unreported | mean. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 210–800 µg/kg (range) | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 330–1,130 µg/kg (range) | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 340–870 µg/kg (range) | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 490–1,380 µg/kg (range) | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 50–310 µg/kg (range) | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 80–890 µg/kg (range) | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | median.Same samples: 340–430 µg/kg (range) | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | range. | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | median.Same samples: 410–1,700 µg/kg (range) | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | range. | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | median.Same samples: 410–1,160 µg/kg (range) | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | range. | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | median.Same samples: 420–1,700 µg/kg (range) | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | range. | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | median.Same samples: 620–1,270 µg/kg (range) | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | range. | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | median.Same samples: 280–2,010 µg/kg (range) | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | range. | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | median.Same samples: 280–950 µg/kg (range) | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | range. | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | median.Same samples: 380–2,010 µg/kg (range) | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | range. | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | median.Same samples: 350–1,420 µg/kg (range) | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | range. | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | median.Same samples: 350–470 µg/kg (range) | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | range. | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | median.Same samples: 430–1,420 µg/kg (range) | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | range. | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | median.Same samples: 230–1,800 µg/kg (range) | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | range. | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | median.Same samples: 90–300 µg/kg (range) | ||
| Tuna · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | range. | ||
| Bonito · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 2,080 µg/kg (maximum) | ||
| Bonito · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Bonito · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Bonito · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Bonito · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Bonito · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Bonito · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Bonito · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Bonito · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Bonito · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Swordfish · fresh or rawBlanco et al. 2023 | various2011–2017basis not stated | median. | ||
| Swordfish · fresh or rawBlanco et al. 2023 | various2011–2017basis not stated | mean.Same samples: 70–2,700 µg/kg (range) | ||
| Swordfish · fresh or rawBlanco et al. 2023 | various2011–2017basis not stated | median. | ||
| Swordfish · fresh or rawBlanco et al. 2023 | various2011–2017basis not stated | range. | ||
| Swordfish · fresh or rawBlanco et al. 2023 | various2011–2017basis not stated | median. | ||
| Swordfish · fresh or rawBlanco et al. 2023 | various2011–2017basis not stated | median. | ||
| Swordfish · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | geometric mean.Same samples: 160–2,730 µg/kg (range) | ||
| Swordfish · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | range. | ||
| Swordfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 6,760 µg/kg (maximum) | ||
| Swordfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Swordfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Swordfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Swordfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Swordfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Swordfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Swordfish · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 268–432 µg/kg (range) | ||
| Swordfish · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Swordfish · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | mean.Same samples: 2,900 µg/kg (maximum) | ||
| Swordfish · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | median. | ||
| Swordfish · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | max. | ||
| Swordfish · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | mean.Same samples: 1,300–2,900 µg/kg (range) | ||
| Swordfish · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | range. | ||
| Swordfish · fresh or rawHandayani et al. 2019 | southern Indian Ocean2012–2017basis not stated | mean. | ||
| Swordfish · fresh or rawHandayani et al. 2019 | western Pacific Ocean2012–2017basis not stated | mean. | ||
| Swordfish · fresh or rawHandayani et al. 2019 | western Pacific Ocean2012–2017basis not stated | range. | ||
| Swordfish · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Swordfish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Swordfish · fresh or rawMehouel et al. 2019 | coast of Algiers, Algeria2017 | mean.Same samples: 250–1,250 µg/kg (range) | ||
| Swordfish · fresh or rawMehouel et al. 2019 | coast of Algiers, Algeria2017 | range. | ||
| Swordfish · fresh or rawMehouel et al. 2019 | Algerian coasts2017 | mean.Same samples: 160–2,180 µg/kg (range) | ||
| Swordfish · fresh or rawMehouel et al. 2019 | Algerian coasts2017 | range. | ||
| Swordfish · fresh or rawMehouel et al. 2019 | coast of Bejaia, Algeria2017 | mean.Same samples: 160–2,180 µg/kg (range) | ||
| Swordfish · fresh or rawMehouel et al. 2019 | coast of Bejaia, Algeria2017 | range. | ||
| Swordfish · fresh or rawMehouel et al. 2019 | coast of Oran, Algeria2017 | mean.Same samples: 190–270 µg/kg (range) | ||
| Swordfish · fresh or rawMehouel et al. 2019 | coast of Oran, Algeria2017 | range. | ||
| Swordfish · fresh or rawOktariani et al. 2023 | FAO Fishing Zone 572012–2016 | range. | ||
| Swordfish · fresh or rawOktariani et al. 2023 | FAO Fishing Zone 712012–2016 | range. | ||
| Swordfish · fresh or rawOlmedo et al. 2013 | Galicia, Spain2009–2010 | median. | ||
| Swordfish · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 380–720 µg/kg (range) | ||
| Swordfish · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Swordfish · fresh or rawSimultaneous speciation… 2023 | Pacific and Indian OceansCollection date unreported | mean. | ||
| Swordfish · fresh or rawSpecies-specific… 2025 | Reunion Islands, Indian Ocean2013–2022 | mean.Same samples: 150–990 µg/kg (range) | ||
| Swordfish · fresh or rawSpecies-specific… 2025 | Reunion Islands, Indian Ocean2013–2022 | range. | ||
| Swordfish · fresh or rawSpecies-specific… 2025 | Seychelles, Indian Ocean2013–2022 | mean.Same samples: 210–1,790 µg/kg (range) | ||
| Swordfish · fresh or rawSpecies-specific… 2025 | Seychelles, Indian Ocean2013–2022 | range. | ||
| Swordfish · fresh or rawSpecies-specific… 2025 | South Africa, Indian Ocean2013–2022 | mean.Same samples: 270–1,130 µg/kg (range) | ||
| Swordfish · fresh or rawSpecies-specific… 2025 | South Africa, Indian Ocean2013–2022 | range. | ||
| Swordfish · fresh or rawSpecies-specific… 2025 | New Caledonia, Pacific Ocean2013–2022 | sample value. | ||
| Swordfish · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 1,240–1,880 µg/kg (range) | ||
| Swordfish · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Swordfish · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Swordfish · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | sample value. | ||
| Marlin and other billfish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Marlin and other billfish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Marlin and other billfish · fresh or rawSmolikova et al. 2016 | Brno City markets, Czech Republic2015–2016 | mean. | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | New Caledonia, Pacific Ocean2013–2022 | mean.Same samples: 3,230–5,380 µg/kg (range) | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | New Caledonia, Pacific Ocean2013–2022 | range. | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | Mauritius, Indian Ocean2013–2022 | mean.Same samples: 620–7,490 µg/kg (range) | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | Mauritius, Indian Ocean2013–2022 | range. | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | New Caledonia, Pacific Ocean2013–2022 | mean.Same samples: 1,300–9,230 µg/kg (range) | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | New Caledonia, Pacific Ocean2013–2022 | range. | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | New Caledonia, Pacific Ocean2013–2022 | mean.Same samples: 350–1,170 µg/kg (range) | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | New Caledonia, Pacific Ocean2013–2022 | range. | ||
| Shark · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | mean.Same samples: 430–2,780 µg/kg (range) | ||
| Shark · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | range. | ||
| Shark · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | sample value. | ||
| Shark · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | geometric mean.Same samples: 160–270 µg/kg (range) | ||
| Shark · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | range. | ||
| Shark · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | geometric mean.Same samples: 1,760–2,290 µg/kg (range) | ||
| Shark · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | range. | ||
| Shark · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | geometric mean.Same samples: 60–840 µg/kg (range) | ||
| Shark · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | range. | ||
| Shark · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | geometric mean.Same samples: 60–4,460 µg/kg (range) | ||
| Shark · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | range. | ||
| Shark · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Shark · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Shark · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Shark · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Shark · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Shark · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Shark · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Shark · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 5,560 µg/kg (maximum) | ||
| Shark · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Shark · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Shark · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Shark · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Shark · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Shark · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Shark · fresh or rawEuropean et al. 2004 | Italy national submission to SCOOP1990–2002basis not stated | mean. | ||
| Shark · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | mean.Same samples: 3,800 µg/kg (maximum) | ||
| Shark · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | median. | ||
| Shark · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | max. | ||
| Shark · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | mean.Same samples: 1,300–3,800 µg/kg (range) | ||
| Shark · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | range. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Mediterranean Sea2017–2022basis not stated | range. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Mediterranean Sea2017–2022basis not stated | mean. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Mediterranean Sea2017–2022basis not stated | mean. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Mediterranean Sea2017–2022basis not stated | mean. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Atlantic Ocean FAO 47-34 and 272017–2022basis not stated | range. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Mediterranean Sea2017–2022basis not stated | max. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Indian Ocean2017–2022basis not stated | range. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Indian Ocean2017–2022basis not stated | range. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Indian Ocean2017–2022basis not stated | range. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Indian Ocean2017–2022basis not stated | range. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Indian Ocean2017–2022basis not stated | range. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Indian Ocean2017–2022basis not stated | range. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Indian Ocean2017–2022basis not stated | range. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Atlantic Ocean FAO 47-34 and 272017–2022basis not stated | range. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Mediterranean Sea2017–2022basis not stated | mean. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Mediterranean Sea2017–2022basis not stated | max. | ||
| Shark · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 63.6–169 µg/kg (range) | ||
| Shark · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Shark · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Shark · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Shark · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Shark · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Shark · fresh or rawnutrients in commercial… 2025 | Gulf of Maine, USA2018 | max. | ||
| Shark · fresh or rawOlmedo et al. 2013 | Basque Country, Spain2009–2010 | median. | ||
| Shark · fresh or rawOlmedo et al. 2013 | Valencia, Spain2009–2010 | median. | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 690–2,140 µg/kg (range) | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 460–1,810 µg/kg (range) | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Shark · fresh or rawSimultaneous speciation… 2023 | FranceCollection date unreported | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 1,350 µg/kg (maximum) | ||
| Ray and skate · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Ray and skate · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Ray and skate · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Ray and skate · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Ray and skate · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Ray and skate · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Ray and skate · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 70–90 µg/kg (range) | ||
| Ray and skate · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Ray and skate · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 30–100 µg/kg (range) | ||
| Ray and skate · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Ray and skate · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Ray and skate · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Ray and skate · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Ray and skate · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Ray and skate · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Ray and skate · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Ray and skate · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Ray and skate · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Ray and skate · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Ray and skate · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Ray and skate · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Ray and skate · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region EURO2004–2020 | median. | ||
| Mackerel · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Mackerel · fresh or rawBrodziak-Dopierala et al. 2023 | FAO 27, North Sea2021–2022basis not stated | mean. | ||
| Mackerel · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 35–64 µg/kg (range) | ||
| Mackerel · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Mackerel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 1,560 µg/kg (maximum) | ||
| Mackerel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Mackerel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Mackerel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Mackerel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Mackerel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Mackerel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Mackerel · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 20–80 µg/kg (range) | ||
| Mackerel · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Mackerel · fresh or rawEuropean et al. 2004 | Italy national submission to SCOOP1990–2002basis not stated | mean. | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 20–52 µg/kg (range) | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 10–80 µg/kg (range) | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Mackerel · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 12.5–30 µg/kg (range) | ||
| Mackerel · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Mackerel · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Mackerel · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Mackerel · fresh or rawKurniawati et al. 2021 | five traditional markets inCollection date unreported | mean. | ||
| Mackerel · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Mackerel · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Mackerel · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Mackerel · fresh or rawMercury intake via… 2020 | Northeast Atlantic2018 | range. | ||
| Mackerel · fresh or rawMercury intake via… 2020 | Northeast Atlantic2018 | mean. | ||
| Mackerel · fresh or rawMercury intake via… 2020 | Northeast Atlantic2018 | mean. | ||
| Mackerel · fresh or rawMercury intake via… 2020 | Northeast Atlantic2018 | mean. | ||
| Mackerel · fresh or rawMercury intake via… 2020 | Northeast Atlantic2018 | mean. | ||
| Mackerel · fresh or rawMercury intake via… 2020 | Northeast Atlantic2018 | mean. | ||
| Mackerel · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Mackerel · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Mackerel · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Mackerel · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Mackerel · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Mackerel · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Mackerel · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Mackerel · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Mackerel · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Mackerel · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Mackerel · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Mackerel · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Mackerel · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Mackerel · fresh or rawTotal Mercury and Fatty… 2022 | Atlantic OceanCollection date unreported | mean. | ||
| Mackerel · fresh or rawVera et al. 2018 | Atlantic OceanCollection date unreported | mean. | ||
| Mackerel · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 40–270 µg/kg (range) | ||
| Mackerel · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Mackerel · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| King and Spanish mackerel · fresh or rawAl-Sulaiti et al. 2023 | Local, wild2021–2022dry weight | mean.Same samples: 60–161 µg/kg (range) | ||
| King and Spanish mackerel · fresh or rawAl-Sulaiti et al. 2023 | Local, wild2021–2022 | mean. | ||
| King and Spanish mackerel · fresh or rawAl-Sulaiti et al. 2023 | Local, wild2021–2022 | range. | ||
| King and Spanish mackerel · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 8–33 µg/kg (range) | ||
| King and Spanish mackerel · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| King and Spanish mackerel · fresh or rawKimakova et al. 2018 | food retailers in Eastern SlovakiaCollection date unreportedbasis not stated | max. | ||
| King and Spanish mackerel · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| King and Spanish mackerel · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| King and Spanish mackerel · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| King and Spanish mackerel · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| King and Spanish mackerel · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| King and Spanish mackerel · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 20–90 µg/kg (range) | ||
| King and Spanish mackerel · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| King and Spanish mackerel · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Horse mackerel, jacks and trevally · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 170 µg/kg (maximum) | ||
| Horse mackerel, jacks and trevally · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Horse mackerel, jacks and trevally · fresh or rawHolbert et al. 2023 | Nearshore waters2015–2016 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawHolbert et al. 2023 | Nearshore waters2015–2016 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | not detected. | ||
| Horse mackerel, jacks and trevally · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Horse mackerel, jacks and trevally · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Horse mackerel, jacks and trevally · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreporteddry weight | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreported | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawOlmedo et al. 2013 | Valencia, Spain2009–2010 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawProducts et al. 2019 | South African retail storesCollection date unreported | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 100–360 µg/kg (range) | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 30–210 µg/kg (range) | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 60–210 µg/kg (range) | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 250–930 µg/kg (range) | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 40–150 µg/kg (range) | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Herring · fresh or rawWHO GEMS/Food | WHO region EURO2004–2020 | median. | ||
| Herring · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 400 µg/kg (maximum) | ||
| Herring · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Herring · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Herring · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Herring · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Herring · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Herring · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Herring · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: up to 107 µg/kg (range maximum) | ||
| Herring · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Herring · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 40–100 µg/kg (range) | ||
| Herring · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Herring · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Herring · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 30–30 µg/kg (range) | ||
| Herring · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Herring · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Herring · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean. | ||
| Herring · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Herring · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Herring · fresh or rawGerman 2024 | Germany2012–2021basis not stated | mean.Same samples: 120 µg/kg (maximum) | ||
| Herring · fresh or rawGerman 2024 | Germany2012–2021basis not stated | max. | ||
| Herring · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 9.2–98 µg/kg (range) | ||
| Herring · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Herring · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Herring · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Herring · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region EURO2004–2018 | median. | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | northern sector2018 | mean. | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | northern sector2018 | range. | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | southern sector2018 | mean. | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | southern sector2018 | range. | ||
| Sardine and pilchard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 244 µg/kg (maximum) | ||
| Sardine and pilchard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sardine and pilchard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sardine and pilchard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sardine and pilchard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sardine and pilchard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sardine and pilchard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 20–50 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 29–38 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 10–101 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 10–160 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Sardine and pilchard · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Sardine and pilchard · fresh or rawMehouel et al. 2019 | coast of Algiers, Algeria2017 | mean.Same samples: 10–60 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawMehouel et al. 2019 | coast of Algiers, Algeria2017 | range. | ||
| Sardine and pilchard · fresh or rawMehouel et al. 2019 | Algerian coasts2017 | mean.Same samples: 10–120 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawMehouel et al. 2019 | Algerian coasts2017 | range. | ||
| Sardine and pilchard · fresh or rawMehouel et al. 2019 | coast of Bejaia, Algeria2017 | mean.Same samples: 70–120 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawMehouel et al. 2019 | coast of Bejaia, Algeria2017 | range. | ||
| Sardine and pilchard · fresh or rawMehouel et al. 2019 | coast of Oran, Algeria2017 | mean.Same samples: 10–30 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawMehouel et al. 2019 | coast of Oran, Algeria2017 | range. | ||
| Sardine and pilchard · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Sardine and pilchard · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Sardine and pilchard · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Sardine and pilchard · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Sardine and pilchard · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 20–30 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Sardine and pilchard · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Sardine and pilchard · fresh or rawYamashita 2024 | Japan2022–2023basis not stated | sample value. | ||
| Sprat · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 117 µg/kg (maximum) | ||
| Sprat · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sprat · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sprat · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sprat · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sprat · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sprat · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Sprat · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Sprat · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 5–30 µg/kg (range) | ||
| Sprat · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Anchovy · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 4–10 µg/kg (range) | ||
| Anchovy · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Anchovy · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 1,250 µg/kg (maximum) | ||
| Anchovy · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Anchovy · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Anchovy · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Anchovy · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Anchovy · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Anchovy · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Anchovy · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Anchovy · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Anchovy · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 10–130 µg/kg (range) | ||
| Anchovy · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Anchovy · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Anchovy · fresh or rawEuropean et al. 2004 | Italy national submission to SCOOP1990–2002basis not stated | mean. | ||
| Anchovy · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Anchovy · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | not detected. | ||
| Anchovy · fresh or rawOlmedo et al. 2013 | Catalonia, Spain2009–2010 | median. | ||
| Anchovy · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Anchovy · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Anchovy · fresh or rawSimionov et al. 2023 | Fishing, Black Sea, BulgariaCollection date unreported | mean. | ||
| Shad, hilsa and other herrings · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 9–15 µg/kg (range) | ||
| Shad, hilsa and other herrings · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Shad, hilsa and other herrings · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Shad, hilsa and other herrings · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 173 µg/kg (maximum) | ||
| Shad, hilsa and other herrings · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Shad, hilsa and other herrings · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Shad, hilsa and other herrings · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Shad, hilsa and other herrings · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Shad, hilsa and other herrings · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Shad, hilsa and other herrings · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Shad, hilsa and other herrings · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Shad, hilsa and other herrings · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | mean.Same samples: 84.1–92.6 µg/kg (range) | ||
| Shad, hilsa and other herrings · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | range. | ||
| Shad, hilsa and other herrings · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | mean.Same samples: 87.4–99.9 µg/kg (range) | ||
| Shad, hilsa and other herrings · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | range. | ||
| Shad, hilsa and other herrings · fresh or rawMelnyk et al. 2021 | Penobscot River and estuary2017–2018 | mean. | ||
| Shad, hilsa and other herrings · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | mean.Same samples: 59.4–73.2 µg/kg (range) | ||
| Shad, hilsa and other herrings · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | range. | ||
| Shad, hilsa and other herrings · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | mean.Same samples: 65.9–86.3 µg/kg (range) | ||
| Shad, hilsa and other herrings · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | range. | ||
| Shad, hilsa and other herrings · fresh or rawMelnyk et al. 2021 | Penobscot River and estuary2017–2018 | mean. | ||
| Shad, hilsa and other herrings · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | mean.Same samples: 36.6–44.3 µg/kg (range) | ||
| Shad, hilsa and other herrings · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | range. | ||
| Shad, hilsa and other herrings · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | mean.Same samples: 58–64.8 µg/kg (range) | ||
| Shad, hilsa and other herrings · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | range. | ||
| Shad, hilsa and other herrings · fresh or rawMelnyk et al. 2021 | Penobscot River and estuary2017–2018 | mean. | ||
| Shad, hilsa and other herrings · fresh or rawMethylmercury… 2021 | Lake Maggiore, Pallanza Basin2016–2017dry weight | mean. | ||
| Shad, hilsa and other herrings · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Shad, hilsa and other herrings · fresh or rawZolfaghari 2018 | Caspian Sea, IranCollection date unreporteddry weight | mean.Same samples: 6–17 µg/kg (range) | ||
| Shad, hilsa and other herrings · fresh or rawZolfaghari 2018 | Caspian Sea, IranCollection date unreporteddry weight | range. | ||
| Salmon · fresh or rawAl-Sulaiti et al. 2023 | Imported2021–2022dry weight | mean.Same samples: 4–14 µg/kg (range) | ||
| Salmon · fresh or rawAl-Sulaiti et al. 2023 | Imported2021–2022 | mean. | ||
| Salmon · fresh or rawAl-Sulaiti et al. 2023 | Imported2021–2022 | range. | ||
| Salmon · fresh or rawBrodziak-Dopierala et al. 2023 | FAO 61/67 n=1; farmed Norway n=22021–2022basis not stated | mean. | ||
| Salmon · fresh or rawBrodziak-Dopierala et al. 2023 | farmed, Norway2021–2022basis not stated | mean. | ||
| Salmon · fresh or rawBrodziak-Dopierala et al. 2023 | FAO 612021–2022basis not stated | mean. | ||
| Salmon · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 20–50 µg/kg (range) | ||
| Salmon · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Salmon · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 20–80 µg/kg (range) | ||
| Salmon · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Salmon · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 46–96 µg/kg (range) | ||
| Salmon · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Salmon · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 20–90 µg/kg (range) | ||
| Salmon · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Salmon · fresh or rawEuropean et al. 2004 | Italy national submission to SCOOP1990–2002basis not stated | mean. | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 31–40 µg/kg (range) | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 10–80 µg/kg (range) | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Salmon · fresh or rawGerman 2024 | Germany2012–2021basis not stated | mean.Same samples: 90 µg/kg (maximum) | ||
| Salmon · fresh or rawGerman 2024 | Germany2012–2021basis not stated | max. | ||
| Salmon · fresh or rawOlmedo et al. 2013 | Norway2009–2010 | below LOD. | ||
| Salmon · fresh or rawPCBs and Heavy Metals… 2020 | caught at sea off Finnmark2017–2018 | mean. | ||
| Salmon · fresh or rawPCBs and Heavy Metals… 2020 | Lerøy Aurora farm2017–2018 | mean. | ||
| Salmon · fresh or rawPCBs and Heavy Metals… 2020 | Lopphavet, Finnmark, Norway2017–2018 | mean. | ||
| Salmon · fresh or rawSelenium: 2021 | Lake Ontario, Great Lakes, USA2017 | mean.Same samples: 106–143 µg/kg (range) | ||
| Salmon · fresh or rawSelenium: 2021 | Lake Ontario, Great Lakes, USA2017 | median. | ||
| Salmon · fresh or rawSelenium: 2021 | Lake Ontario, Great Lakes, USA2017 | range. | ||
| Salmon · fresh or rawSelenium: 2021 | Lake Ontario, Great Lakes, USA2017 | mean.Same samples: 119–172 µg/kg (range) | ||
| Salmon · fresh or rawSelenium: 2021 | Lake Ontario, Great Lakes, USA2017 | median. | ||
| Salmon · fresh or rawSelenium: 2021 | Lake Ontario, Great Lakes, USA2017 | range. | ||
| Salmon · fresh or rawSimionov et al. 2023 | Aquaculture, NorwayCollection date unreported | mean. | ||
| Salmon · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Salmon · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Salmon · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: up to 140 µg/kg (range maximum) | ||
| Salmon · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Salmon · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region EURO2004–2020 | median. | ||
| Trout and char · fresh or rawBrodziak-Dopierala et al. 2023 | Poland retail and direct from2021–2022basis not stated | mean. | ||
| Trout and char · fresh or rawBrodziak-Dopierala et al. 2023 | Poland retail and direct from2021–2022basis not stated | mean. | ||
| Trout and char · fresh or rawDietz et al. 2025 | lake at South Greenland AMAP site1983–2024 | median. | ||
| Trout and char · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Trout and char · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 40 µg/kg (maximum) | ||
| Trout and char · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Trout and char · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Trout and char · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Trout and char · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Trout and char · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Trout and char · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Trout and char · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: up to 48 µg/kg (range maximum) | ||
| Trout and char · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Trout and char · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Trout and char · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 25.6–100 µg/kg (range) | ||
| Trout and char · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Trout and char · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 10–20 µg/kg (range) | ||
| Trout and char · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Trout and char · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Trout and char · fresh or rawGerman 2024 | Germany2012–2021basis not stated | mean.Same samples: 140 µg/kg (maximum) | ||
| Trout and char · fresh or rawGerman 2024 | Germany2012–2021basis not stated | max. | ||
| Trout and char · fresh or rawGroleau et al. 2025 | Nunavik, Quebec, CanadaCollection date unreported | max. | ||
| Trout and char · fresh or rawLehel et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | below LOD. | ||
| Trout and char · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | not detected. | ||
| Trout and char · fresh or rawMajlesi et al. 2017 | Khersan River2016basis not stated | mean. | ||
| Trout and char · fresh or rawMajlesi et al. 2019 | Six raceway farms in three culture2018dry weight | mean. | ||
| Trout and char · fresh or rawMajlesi et al. 2019 | Site A2018dry weight | mean. | ||
| Trout and char · fresh or rawMajlesi et al. 2019 | Site B2018dry weight | mean. | ||
| Trout and char · fresh or rawMajlesi et al. 2019 | Site C2018dry weight | mean. | ||
| Trout and char · fresh or rawRundio et al. 2022 | Big Creek2005–2020dry weight | geometric mean. | ||
| Trout and char · fresh or rawRundio et al. 2022 | Big Creek2005–2020dry weight | geometric mean. | ||
| Trout and char · fresh or rawSelenium: 2021 | Lake Michigan, Great Lakes, USA2017 | mean.Same samples: 81–211 µg/kg (range) | ||
| Trout and char · fresh or rawSelenium: 2021 | Lake Michigan, Great Lakes, USA2017 | median. | ||
| Trout and char · fresh or rawSelenium: 2021 | Lake Michigan, Great Lakes, USA2017 | range. | ||
| Trout and char · fresh or rawSelenium: 2021 | Lake Michigan, Great Lakes, USA2017 | mean.Same samples: 95.2–222 µg/kg (range) | ||
| Trout and char · fresh or rawSelenium: 2021 | Lake Michigan, Great Lakes, USA2017 | median. | ||
| Trout and char · fresh or rawSelenium: 2021 | Lake Michigan, Great Lakes, USA2017 | range. | ||
| Trout and char · fresh or rawSETAC EUROPE 35 TH… 2025 | 13 streamsCollection date unreporteddry weight | range. | ||
| Trout and char · fresh or rawSimionov et al. 2023 | Aquaculture, RomaniaCollection date unreported | mean. | ||
| Trout and char · fresh or rawSimultaneous speciation… 2023 | ANSES aquaculture facilitiesCollection date unreported | mean. | ||
| Trout and char · fresh or rawTotal Mercury and Fatty… 2022 | Lakes in CanadaCollection date unreported | mean. | ||
| Trout and char · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: up to 20 µg/kg (range maximum) | ||
| Trout and char · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Trout and char · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Whitefish and vendace · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | mean.Same samples: 50–139 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | median. | ||
| Whitefish and vendace · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | range. | ||
| Whitefish and vendace · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | mean.Same samples: 54–81 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | median. | ||
| Whitefish and vendace · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | range. | ||
| Whitefish and vendace · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | min. | ||
| Whitefish and vendace · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Whitefish and vendace · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 260 µg/kg (maximum) | ||
| Whitefish and vendace · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Whitefish and vendace · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Whitefish and vendace · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Whitefish and vendace · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Whitefish and vendace · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Whitefish and vendace · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Whitefish and vendace · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 61–96 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Whitefish and vendace · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 19–137 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 42–156 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | not detected. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 44–184 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 5–15 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 84–240 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 14–39 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 156–595 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 25–56 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 104–226 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 28–64 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 118–276 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 42–104 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 201–791 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 69–349 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 101–341 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 24–102 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 165–480 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 61–165 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 180–394 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 49–134 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 94–404 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 36–125 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 128–346 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 38–96 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 143–469 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 21–140 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 144–506 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 17–106 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 155–439 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 15–111 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Whitefish and vendace · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Whitefish and vendace · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Whitefish and vendace · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Whitefish and vendace · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region EURO2004–2020 | median. | ||
| Cod · fresh or rawBrodziak-Dopierala et al. 2023 | FAO 27, Norwegian Sea2021–2022basis not stated | mean. | ||
| Cod · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 10–190 µg/kg (range) | ||
| Cod · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Cod · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 30–110 µg/kg (range) | ||
| Cod · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Cod · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Cod · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 19.7–79.2 µg/kg (range) | ||
| Cod · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Cod · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Cod · fresh or rawOlmedo et al. 2013 | Atlantic Northeast2009–2010 | below LOD. | ||
| Cod · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Cod · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 20–200 µg/kg (range) | ||
| Cod · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Cod · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Haddock · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 10–270 µg/kg (range) | ||
| Haddock · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Haddock · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 40–60 µg/kg (range) | ||
| Haddock · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Haddock · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Haddock · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Haddock · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 19–68.9 µg/kg (range) | ||
| Haddock · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Haddock · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Pollock and saithe · fresh or rawBrodziak-Dopierala et al. 2023 | FAO 61, FAO 67, Pacific Ocean2021–2022basis not stated | mean. | ||
| Pollock and saithe · fresh or rawBrodziak-Dopierala et al. 2023 | FAO 27, North Sea2021–2022basis not stated | mean. | ||
| Pollock and saithe · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 11–35 µg/kg (range); 11–44 µg/kg (range) | ||
| Pollock and saithe · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean. | ||
| Pollock and saithe · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Pollock and saithe · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Pollock and saithe · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 50–50 µg/kg (range) | ||
| Pollock and saithe · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Pollock and saithe · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 50–200 µg/kg (range) | ||
| Pollock and saithe · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Pollock and saithe · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 250–250 µg/kg (range) | ||
| Pollock and saithe · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Pollock and saithe · fresh or rawGerman 2024 | Germany2012–2021basis not stated | mean.Same samples: 180 µg/kg (maximum) | ||
| Pollock and saithe · fresh or rawGerman 2024 | Germany2012–2021basis not stated | max. | ||
| Pollock and saithe · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 10.4–32 µg/kg (range) | ||
| Pollock and saithe · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Pollock and saithe · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara, 8 stations2019 | mean.Same samples: 307–640 µg/kg (range) | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara, 8 stations2019 | range. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L12019 | mean. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L22019 | mean. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L32019 | mean. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L52019 | mean. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L72019 | mean. | ||
| Whiting and blue whiting · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 10–200 µg/kg (range) | ||
| Whiting and blue whiting · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Whiting and blue whiting · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 20–20 µg/kg (range) | ||
| Whiting and blue whiting · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Whiting and blue whiting · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 20–90 µg/kg (range) | ||
| Whiting and blue whiting · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Whiting and blue whiting · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Whiting and blue whiting · fresh or rawOlmedo et al. 2013 | Galicia, Spain2009–2010 | median. | ||
| Hake · fresh or rawBrodziak-Dopierala et al. 2023 | FAO 412021–2022basis not stated | mean. | ||
| Hake · fresh or rawDjedjibegovic et al. 2020 | Spain2019 | mean.Same samples: 22–25 µg/kg (range) | ||
| Hake · fresh or rawDjedjibegovic et al. 2020 | Spain2019 | range. | ||
| Hake · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 660 µg/kg (maximum) | ||
| Hake · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Hake · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Hake · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Hake · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Hake · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Hake · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Hake · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 30–150 µg/kg (range) | ||
| Hake · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Hake · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 40–60 µg/kg (range) | ||
| Hake · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Hake · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Hake · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 23–43.9 µg/kg (range) | ||
| Hake · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Hake · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Hake · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Hake · fresh or rawOlmedo et al. 2013 | Valencia, Spain2009–2010 | median. | ||
| Hake · fresh or rawOlmedo et al. 2013 | Mauritania2009–2010 | median. | ||
| Hake · fresh or rawOlmedo et al. 2013 | Mauritania2009–2010 | below LOD. | ||
| Hake · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Hake · fresh or rawSimionov et al. 2023 | Spain; fishing area not specifiedCollection date unreported | mean. | ||
| Hake · fresh or rawVera et al. 2018 | South AfricaCollection date unreported | mean. | ||
| Hake · fresh or rawVera et al. 2018 | South AmericaCollection date unreported | mean. | ||
| Ling, tusk and other cod-like fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 137 µg/kg (maximum) | ||
| Ling, tusk and other cod-like fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Ling, tusk and other cod-like fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Ling, tusk and other cod-like fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Ling, tusk and other cod-like fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Ling, tusk and other cod-like fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Ling, tusk and other cod-like fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Ling, tusk and other cod-like fish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 90–90 µg/kg (range) | ||
| Ling, tusk and other cod-like fish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Ling, tusk and other cod-like fish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 110–290 µg/kg (range) | ||
| Ling, tusk and other cod-like fish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Ling, tusk and other cod-like fish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 160–160 µg/kg (range) | ||
| Ling, tusk and other cod-like fish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Ling, tusk and other cod-like fish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Ling, tusk and other cod-like fish · fresh or rawReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Ling, tusk and other cod-like fish · fresh or rawRohonczy et al. 2024 | near Inukjuak2014–2017dry weight | mean. | ||
| Ling, tusk and other cod-like fish · fresh or rawRohonczy et al. 2024 | near Kuujjuaraapik2014–2017dry weight | mean. | ||
| Ling, tusk and other cod-like fish · fresh or rawRohonczy et al. 2024 | near Sanikiluaq2014–2017dry weight | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawBrodziak-Dopierala et al. 2023 | FAO 272021–2022basis not stated | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawBrodziak-Dopierala et al. 2023 | FAO 272021–2022basis not stated | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 578 µg/kg (maximum) | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 400 µg/kg (maximum) | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 500 µg/kg (maximum) | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 89 µg/kg (maximum) | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 30–210 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 20–150 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 30–140 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 10–190 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 20–330 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 10–100 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Italy national submission to SCOOP1990–2002basis not stated | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 20–60 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Italy national submission to SCOOP1990–2002basis not stated | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 130–270 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 80–90 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawGerman 2024 | Germany2012–2021basis not stated | mean.Same samples: 190 µg/kg (maximum) | ||
| Plaice, flounder, sole and turbot · fresh or rawGerman 2024 | Germany2012–2021basis not stated | max. | ||
| Plaice, flounder, sole and turbot · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 9.4–32.7 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 12–50.7 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | not detected. | ||
| Plaice, flounder, sole and turbot · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | not detected. | ||
| Plaice, flounder, sole and turbot · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawOlmedo et al. 2013 | Morocco2009–2010 | below LOD. | ||
| Plaice, flounder, sole and turbot · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawTotal Mercury and Fatty… 2022 | Baltic SeaCollection date unreported | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawVera et al. 2018 | ChannelCollection date unreported | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawVera et al. 2018 | Goro, ItalyCollection date unreported | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 20–500 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Halibut · fresh or rawBrodziak-Dopierala et al. 2023 | FAO 27, FAO 212021–2022basis not stated | mean. | ||
| Halibut · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 2,280 µg/kg (maximum) | ||
| Halibut · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Halibut · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Halibut · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Halibut · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Halibut · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Halibut · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Halibut · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Sea bass and barramundi · fresh or rawAl-Sulaiti et al. 2023 | Imported, farmed2021–2022dry weight | mean.Same samples: 12–30 µg/kg (range) | ||
| Sea bass and barramundi · fresh or rawAl-Sulaiti et al. 2023 | Imported, farmed2021–2022 | mean. | ||
| Sea bass and barramundi · fresh or rawAl-Sulaiti et al. 2023 | Imported, farmed2021–2022 | range. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 4,170 µg/kg (maximum) | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 610 µg/kg (maximum) | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Sea bass and barramundi · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 30–80 µg/kg (range) | ||
| Sea bass and barramundi · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Sea bass and barramundi · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Sea bass and barramundi · fresh or rawLevent 2022 | Sinop fish markets, Turkey2020 | mean. | ||
| Sea bass and barramundi · fresh or rawLevent 2022 | Sinop fish markets, Turkey2020 | mean. | ||
| Sea bass and barramundi · fresh or rawLevent 2022 | Sinop fish markets, Turkey2020 | mean. | ||
| Sea bass and barramundi · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Sea bass and barramundi · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | mean.Same samples: 131–245 µg/kg (range) | ||
| Sea bass and barramundi · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | range. | ||
| Sea bass and barramundi · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | mean.Same samples: 129–174 µg/kg (range) | ||
| Sea bass and barramundi · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | range. | ||
| Sea bass and barramundi · fresh or rawMelnyk et al. 2021 | Penobscot River and estuary2017–2018 | mean. | ||
| Sea bass and barramundi · fresh or rawOlmedo et al. 2013 | Murcia, Spain2009–2010 | median. | ||
| Sea bass and barramundi · fresh or rawRay et al. 2025 | coastal and inland watersCollection date unreporteddry weight | mean. | ||
| Sea bass and barramundi · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Sea bass and barramundi · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Sea bass and barramundi · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Sea bass and barramundi · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Sea bass and barramundi · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 520–670 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 940–1,450 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 2,910 µg/kg (maximum) | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 4,450 µg/kg (maximum) | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | sample value. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 20.5–90 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 4–114 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 80–231 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Sea bream and porgies · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Sea bream and porgies · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Sea bream and porgies · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Sea bream and porgies · fresh or rawOlmedo et al. 2013 | Murcia, Spain2009–2010 | median. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station I2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station II2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawSimionov et al. 2023 | Aquaculture, GreeceCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawTotal Mercury and Fatty… 2022 | Mediterranean SeaCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawVera et al. 2018 | Farmed, ItalyCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 50–430 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Sea bream and porgies · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Sea bream and porgies · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | not detected. | ||
| Sea bream and porgies · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | not detected. | ||
| Red mullet and goatfish · fresh or rawAkkaya et al. 2025 | Marmara region provinces, Türkiye2020–2022 | mean. | ||
| Red mullet and goatfish · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 1,710–2,110 µg/kg (range) | ||
| Red mullet and goatfish · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Red mullet and goatfish · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station I2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station II2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Grey mullet · fresh or rawBakhshalizadeh et al. 2023 | Southern Caspian SeaCollection date unreportedbasis not stated | median. | ||
| Grey mullet · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 1,000 µg/kg (maximum) | ||
| Grey mullet · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Grey mullet · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Grey mullet · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Grey mullet · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Grey mullet · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Grey mullet · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Grey mullet · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 120–130 µg/kg (range) | ||
| Grey mullet · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Grey mullet · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Grey mullet · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Grey mullet · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Snapper · fresh or rawChristian et al. 2024 | Antigua and Barbuda2005–2023 | geometric mean.Same samples: 30–640 µg/kg (range) | ||
| Snapper · fresh or rawChristian et al. 2024 | Antigua and Barbuda2005–2023 | range. | ||
| Snapper · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Snapper · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Snapper · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Snapper · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Snapper · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Snapper · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Snapper · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Snapper · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Snapper · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Snapper · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Snapper · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Grouper · fresh or rawAl-Sulaiti et al. 2023 | Local and imported combined2021–2022dry weight | mean.Same samples: 89–443 µg/kg (range) | ||
| Grouper · fresh or rawAl-Sulaiti et al. 2023 | Local and imported combined2021–2022 | mean. | ||
| Grouper · fresh or rawAl-Sulaiti et al. 2023 | Local and imported combined2021–2022 | range. | ||
| Grouper · fresh or rawAl-Sulaiti et al. 2023 | Imported2021–2022dry weight | mean.Same samples: 372–443 µg/kg (range) | ||
| Grouper · fresh or rawAl-Sulaiti et al. 2023 | Imported2021–2022 | mean. | ||
| Grouper · fresh or rawAl-Sulaiti et al. 2023 | Imported2021–2022 | range. | ||
| Grouper · fresh or rawAl-Sulaiti et al. 2023 | Local, wild2021–2022dry weight | mean.Same samples: 89–230 µg/kg (range) | ||
| Grouper · fresh or rawAl-Sulaiti et al. 2023 | Local, wild2021–2022 | mean. | ||
| Grouper · fresh or rawAl-Sulaiti et al. 2023 | Local, wild2021–2022 | range. | ||
| Grouper · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | geometric mean.Same samples: 30–3,670 µg/kg (range) | ||
| Grouper · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | range. | ||
| Grouper · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | geometric mean.Same samples: 2,160–3,670 µg/kg (range) | ||
| Grouper · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | range. | ||
| Grouper · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 320 µg/kg (maximum) | ||
| Grouper · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Grouper · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Grouper · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Grouper · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Grouper · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Grouper · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Grouper · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Grouper · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Grouper · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean.Same samples: 550 µg/kg (maximum) | ||
| Grouper · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | max. | ||
| Croaker and drum · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | sample value. | ||
| Croaker and drum · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean.Same samples: 10.8–49.5 µg/kg (range) | ||
| Croaker and drum · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Croaker and drum · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | geometric mean.Same samples: 20–1,220 µg/kg (range) | ||
| Croaker and drum · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | range. | ||
| Croaker and drum · fresh or rawChristian et al. 2024 | Suriname rivers2005–2023 | geometric mean.Same samples: 20–1,220 µg/kg (range) | ||
| Croaker and drum · fresh or rawChristian et al. 2024 | Suriname rivers2005–2023 | range. | ||
| Croaker and drum · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 10–39 µg/kg (range) | ||
| Croaker and drum · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Croaker and drum · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 290 µg/kg (maximum) | ||
| Croaker and drum · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Croaker and drum · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Croaker and drum · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Croaker and drum · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Croaker and drum · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Croaker and drum · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Croaker and drum · fresh or rawFuentes-Lopez et al. 2025 | San Marcos2022–2023 | mean. | ||
| Croaker and drum · fresh or rawFuentes-Lopez et al. 2025 | San Marcos2022–2023 | mean. | ||
| Croaker and drum · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | not detected. | ||
| Croaker and drum · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: 470–1,080 µg/kg (range) | ||
| Croaker and drum · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Croaker and drum · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Croaker and drum · fresh or rawOliveira et al. 2022 | Small lakes around São Luiz do2018–2019 | mean.Same samples: 50–1,370 µg/kg (range) | ||
| Croaker and drum · fresh or rawOliveira et al. 2022 | Small lakes around São Luiz do2018–2019 | median. | ||
| Croaker and drum · fresh or rawOliveira et al. 2022 | Small lakes around São Luiz do2018–2019 | range. | ||
| Croaker and drum · fresh or rawOliveira et al. 2022 | Small lakes around São Luiz do2018–2019 | mean.Same samples: 250–1,650 µg/kg (range) | ||
| Croaker and drum · fresh or rawOliveira et al. 2022 | Small lakes around São Luiz do2018–2019 | median. | ||
| Croaker and drum · fresh or rawOliveira et al. 2022 | Small lakes around São Luiz do2018–2019 | range. | ||
| Croaker and drum · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Croaker and drum · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Croaker and drum · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Croaker and drum · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Croaker and drum · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Croaker and drum · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Croaker and drum · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Croaker and drum · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Croaker and drum · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | not detected. | ||
| Emperors and grunts · fresh or rawAl-Sulaiti et al. 2023 | Local, wild2021–2022dry weight | mean.Same samples: 42–76 µg/kg (range) | ||
| Emperors and grunts · fresh or rawAl-Sulaiti et al. 2023 | Local, wild2021–2022 | mean. | ||
| Emperors and grunts · fresh or rawAl-Sulaiti et al. 2023 | Local, wild2021–2022 | range. | ||
| Emperors and grunts · fresh or rawChristian et al. 2024 | Moruga or Mayaro2005–2023 | geometric mean.Same samples: 340–2,340 µg/kg (range) | ||
| Emperors and grunts · fresh or rawChristian et al. 2024 | Moruga or Mayaro2005–2023 | range. | ||
| Emperors and grunts · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | sample value. | ||
| Emperors and grunts · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | geometric mean.Same samples: 80–250 µg/kg (range) | ||
| Emperors and grunts · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | range. | ||
| Emperors and grunts · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | geometric mean.Same samples: 80–2,340 µg/kg (range) | ||
| Emperors and grunts · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | range. | ||
| Emperors and grunts · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Emperors and grunts · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Pomfret · fresh or rawAlongkote et al. 2025 | not stated2025 | not detected. | ||
| Pomfret · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Pomfret · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Pomfret · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | not detected. | ||
| Hairtail and cutlassfish · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 7–272 µg/kg (range) | ||
| Hairtail and cutlassfish · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Hairtail and cutlassfish · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | not detected. | ||
| Hairtail and cutlassfish · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Hairtail and cutlassfish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Hairtail and cutlassfish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Barracuda · fresh or rawChristian et al. 2024 | Antigua and Barbuda2005–2023 | geometric mean.Same samples: 30–2,530 µg/kg (range) | ||
| Barracuda · fresh or rawChristian et al. 2024 | Antigua and Barbuda2005–2023 | range. | ||
| Barracuda · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Barracuda · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 340 µg/kg (maximum) | ||
| Barracuda · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Barracuda · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Barracuda · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Barracuda · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Barracuda · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Barracuda · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Barracuda · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Barracuda · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Barracuda · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreporteddry weight | mean. | ||
| Barracuda · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreported | mean. | ||
| Barracuda · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Barracuda · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Mahi-mahi · fresh or rawChristian et al. 2024 | Anguilla2005–2023 | geometric mean.Same samples: 10–470 µg/kg (range) | ||
| Mahi-mahi · fresh or rawChristian et al. 2024 | Anguilla2005–2023 | range. | ||
| Mahi-mahi · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Scorpionfish and rockfish · fresh or rawChristian et al. 2024 | Antigua and Barbuda2005–2023 | geometric mean.Same samples: 20–500 µg/kg (range) | ||
| Scorpionfish and rockfish · fresh or rawChristian et al. 2024 | Antigua and Barbuda2005–2023 | range. | ||
| Scorpionfish and rockfish · fresh or rawChristian et al. 2024 | Antigua and Barbuda2005–2023 | geometric mean.Same samples: 40–190 µg/kg (range) | ||
| Scorpionfish and rockfish · fresh or rawChristian et al. 2024 | Antigua and Barbuda2005–2023 | range. | ||
| Scorpionfish and rockfish · fresh or rawChristian et al. 2024 | Dominica2005–2023 | geometric mean.Same samples: 35–230 µg/kg (range) | ||
| Scorpionfish and rockfish · fresh or rawChristian et al. 2024 | Dominica2005–2023 | range. | ||
| Scorpionfish and rockfish · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 69–199 µg/kg (range) | ||
| Scorpionfish and rockfish · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Scorpionfish and rockfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 422 µg/kg (maximum) | ||
| Scorpionfish and rockfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Scorpionfish and rockfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Scorpionfish and rockfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Scorpionfish and rockfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Scorpionfish and rockfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Scorpionfish and rockfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Scorpionfish and rockfish · fresh or rawGerman 2024 | Germany2012–2021basis not stated | mean.Same samples: 550 µg/kg (maximum) | ||
| Scorpionfish and rockfish · fresh or rawGerman 2024 | Germany2012–2021basis not stated | max. | ||
| Scorpionfish and rockfish · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Anglerfish and monkfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 2,900 µg/kg (maximum) | ||
| Anglerfish and monkfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Anglerfish and monkfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Anglerfish and monkfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Anglerfish and monkfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Anglerfish and monkfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Anglerfish and monkfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Anglerfish and monkfish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 80–180 µg/kg (range) | ||
| Anglerfish and monkfish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Anglerfish and monkfish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Anglerfish and monkfish · fresh or rawOlmedo et al. 2013 | Mauritania2009–2010 | median. | ||
| Anglerfish and monkfish · fresh or rawVera et al. 2018 | Atlantic OceanCollection date unreported | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara, 8 stations2019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L12019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L32019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L42019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L52019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L62019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L82019 | mean. | ||
| Gurnard · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Gurnard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 262 µg/kg (maximum) | ||
| Gurnard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Gurnard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Gurnard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Gurnard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Gurnard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Gurnard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Gurnard · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 90–90 µg/kg (range) | ||
| Gurnard · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Gurnard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Eel · fresh or rawASSESSING HUMAN RISKS… 2024 | reservoirCollection date unreported | mean. | ||
| Eel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 1,880 µg/kg (maximum) | ||
| Eel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Eel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Eel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Eel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Eel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Eel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Eel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 20–110 µg/kg (range) | ||
| Eel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Eel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Eel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Eel · fresh or rawGerman 2024 | Germany2012–2021basis not stated | mean.Same samples: 900 µg/kg (maximum) | ||
| Eel · fresh or rawGerman 2024 | Germany2012–2021basis not stated | max. | ||
| Eel · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Eel · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Eel · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Sturgeon · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 86 µg/kg (maximum) | ||
| Sturgeon · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sturgeon · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sturgeon · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sturgeon · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sturgeon · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sturgeon · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Sturgeon · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | not detected. | ||
| Other marine fish · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | mean.Same samples: 30–1,790 µg/kg (range) | ||
| Other marine fish · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | range. | ||
| Other marine fish · fresh or rawAl-Sulaiti et al. 2023 | Local, wild2021–2022basis not stated | below LOD. | ||
| Other marine fish · fresh or rawAlongkote et al. 2025 | not stated2025 | mean. | ||
| Other marine fish · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Other marine fish · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | sample value. | ||
| Other marine fish · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | geometric mean.Same samples: 530–750 µg/kg (range) | ||
| Other marine fish · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | range. | ||
| Other marine fish · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | sample value. | ||
| Other marine fish · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | geometric mean.Same samples: 4–12 µg/kg (range) | ||
| Other marine fish · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | range. | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | mean.Same samples: 43.7–182 µg/kg (range) | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | median. | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | range. | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | mean.Same samples: 5.55–39.1 µg/kg (range) | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | median. | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | range. | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | mean.Same samples: 20.8–176 µg/kg (range) | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | median. | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | range. | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | mean.Same samples: 5.73–34.8 µg/kg (range) | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | median. | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | range. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 10 µg/kg (maximum) | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 1,000 µg/kg (maximum) | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 620 µg/kg (maximum) | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 650 µg/kg (maximum) | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 590 µg/kg (maximum) | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 1,570 µg/kg (maximum) | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 950 µg/kg (maximum) | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 370 µg/kg (maximum) | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 1,930 µg/kg (maximum) | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 1,730 µg/kg (maximum) | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Other marine fish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 70–70 µg/kg (range) | ||
| Other marine fish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Other marine fish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 190–190 µg/kg (range) | ||
| Other marine fish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Other marine fish · fresh or rawFuentes-Lopez et al. 2025 | San Marcos2022–2023 | mean. | ||
| Other marine fish · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 39.9–122 µg/kg (range) | ||
| Other marine fish · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Other marine fish · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Other marine fish · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | not detected. | ||
| Other marine fish · fresh or rawHolbert et al. 2023 | Nearshore waters2015–2016 | mean. | ||
| Other marine fish · fresh or rawHolbert et al. 2023 | Nearshore waters2015–2016 | mean. | ||
| Other marine fish · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Other marine fish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Other marine fish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Other marine fish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Other marine fish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | not detected. | ||
| Other marine fish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Other marine fish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Other marine fish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | not detected. | ||
| Other marine fish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Other marine fish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Other marine fish · fresh or rawMelnyk et al. 2021 | Penobscot River estuary2017–2018 | mean.Same samples: 57.1–182 µg/kg (range) | ||
| Other marine fish · fresh or rawMelnyk et al. 2021 | Penobscot River estuary2017–2018 | range. | ||
| Other marine fish · fresh or rawMelnyk et al. 2021 | Penobscot River and estuary2017–2018 | mean. | ||
| Other marine fish · fresh or rawMelnyk et al. 2021 | Penobscot River spawning streams2017–2018 | mean.Same samples: 137–148 µg/kg (range) | ||
| Other marine fish · fresh or rawMelnyk et al. 2021 | Penobscot River spawning streams2017–2018 | range. | ||
| Other marine fish · fresh or rawMelnyk et al. 2021 | Penobscot River spawning streams2017–2018 | mean.Same samples: 97.3–135 µg/kg (range) | ||
| Other marine fish · fresh or rawMelnyk et al. 2021 | Penobscot River spawning streams2017–2018 | range. | ||
| Other marine fish · fresh or rawMoura et al. 2022 | Aracati2015–2019basis not stated | mean. | ||
| Other marine fish · fresh or rawMoura et al. 2022 | Cabreiro2015–2019basis not stated | mean. | ||
| Other marine fish · fresh or rawMoura et al. 2022 | Jaguaribe River Estuary2015–2019basis not stated | mean. | ||
| Other marine fish · fresh or rawMoura et al. 2022 | Fortim City2015–2019basis not stated | mean. | ||
| Other marine fish · fresh or rawMoura et al. 2022 | Itaiçaba2015–2019basis not stated | mean. | ||
| Other marine fish · fresh or rawMoura et al. 2022 | Jardim2015–2019basis not stated | mean. | ||
| Other marine fish · fresh or rawMoura et al. 2022 | Jaguaribe River Estuary2015–2019basis not stated | mean. | ||
| Other marine fish · fresh or rawMoura et al. 2022 | Vila Volta2015–2019basis not stated | mean. | ||
| Other marine fish · fresh or rawRay et al. 2025 | coastal and inland watersCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawRohonczy et al. 2024 | near Inukjuak2014–2017dry weight | mean. | ||
| Other marine fish · fresh or rawRohonczy et al. 2024 | near Kuujjuaraapik2014–2017dry weight | mean. | ||
| Other marine fish · fresh or rawRohonczy et al. 2024 | near Sanikiluaq2014–2017dry weight | mean. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Other marine fish · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Other marine fish · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Other marine fish · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 50–70 µg/kg (range) | ||
| Other marine fish · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Other marine fish · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Other marine fish · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | not detected. | ||
| Tilapia · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean.Same samples: 1.1–12.4 µg/kg (range) | ||
| Tilapia · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Tilapia · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean.Same samples: 1.2–14.3 µg/kg (range) | ||
| Tilapia · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Tilapia · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | not detected. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Lake zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawPáez-Osuna et al. 2024 | El Comedero dam2013–2014 | mean.Same samples: 20–220 µg/kg (range) | ||
| Tilapia · fresh or rawPáez-Osuna et al. 2024 | El Comedero dam2013–2014 | range. | ||
| Tilapia · fresh or rawPáez-Osuna et al. 2024 | El Comedero dam2013–2014dry weight | mean. | ||
| Tilapia · fresh or rawRay et al. 2025 | coastal and inland watersCollection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawShumba et al. 2025 | Kitwe District mining area: Uchi2023dry weight | mean.Same samples: 0–45 µg/kg (range) | ||
| Tilapia · fresh or rawShumba et al. 2025 | Kitwe District mining area: Uchi2023dry weight | median. | ||
| Tilapia · fresh or rawShumba et al. 2025 | Kitwe District mining area: Uchi2023dry weight | range. | ||
| Tilapia · fresh or rawShumba et al. 2025 | Chilubula2023dry weight | mean.Same samples: 0–54 µg/kg (range) | ||
| Tilapia · fresh or rawShumba et al. 2025 | Chilubula2023dry weight | median. | ||
| Tilapia · fresh or rawShumba et al. 2025 | Chilubula2023dry weight | range. | ||
| Tilapia · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Tilapia · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Tilapia · fresh or rawSmolikova et al. 2016 | Brno City markets, Czech Republic2015–2016 | mean. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Amarat reservoir2022basis not stated | mean.Same samples: 6–14 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Amarat reservoir2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Khawd reservoir2022basis not stated | mean.Same samples: 1–9 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Khawd reservoir2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Surur area2022basis not stated | mean.Same samples: 1–4 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Surur area2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawASSESSING HUMAN RISKS… 2024 | reservoirCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawBrodziak-Dopierala et al. 2023 | farmed, Poland2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | mean.Same samples: 7–88 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | median. | ||
| Carp and other cyprinids · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | range. | ||
| Carp and other cyprinids · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | mean.Same samples: 75–111 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | median. | ||
| Carp and other cyprinids · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | range. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | Rivers Bečva and Svratka2021–2022 | range. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 12021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 22021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 32021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 42021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 430 µg/kg (maximum) | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 985 µg/kg (maximum) | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 240 µg/kg (maximum) | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Carp and other cyprinids · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 80–85 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawGerman 2024 | Germany2012–2021basis not stated | mean.Same samples: 130 µg/kg (maximum) | ||
| Carp and other cyprinids · fresh or rawGerman 2024 | Germany2012–2021basis not stated | max. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Carp and other cyprinids · fresh or rawKimakova et al. 2018 | Ruzin water reservoirCollection date unreportedbasis not stated | max. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | range. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | mean.Same samples: 43–81 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | range. | ||
| Carp and other cyprinids · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawMajlesi et al. 2017 | Khersan River2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawMercury in Selected… 2023 | Lake Insko, north-western PolandCollection date unreported | mean.Same samples: 1–11 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawMercury in Selected… 2023 | Lake Insko, north-western PolandCollection date unreported | range. | ||
| Carp and other cyprinids · fresh or rawMercury in Selected… 2023 | Lake Wisola, north-western PolandCollection date unreported | mean.Same samples: 1–45 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawMercury in Selected… 2023 | Lake Wisola, north-western PolandCollection date unreported | range. | ||
| Carp and other cyprinids · fresh or rawMercury in Selected… 2023 | Lake Insko, north-western PolandCollection date unreported | mean.Same samples: 11–116 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawMercury in Selected… 2023 | Lake Insko, north-western PolandCollection date unreported | range. | ||
| Carp and other cyprinids · fresh or rawMercury in Selected… 2023 | Lake Wisola, north-western PolandCollection date unreported | mean.Same samples: 2–155 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawMercury in Selected… 2023 | Lake Wisola, north-western PolandCollection date unreported | range. | ||
| Carp and other cyprinids · fresh or rawMethylmercury… 2021 | Boesio River mouth2016–2017dry weight | mean. | ||
| Carp and other cyprinids · fresh or rawMethylmercury… 2021 | Boesio River mouth2016–2017dry weight | mean. | ||
| Carp and other cyprinids · fresh or rawPáez-Osuna et al. 2024 | El Comedero dam2013–2014 | mean.Same samples: 40–230 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPáez-Osuna et al. 2024 | El Comedero dam2013–2014 | range. | ||
| Carp and other cyprinids · fresh or rawPáez-Osuna et al. 2024 | El Comedero dam2013–2014dry weight | mean. | ||
| Carp and other cyprinids · fresh or rawRusko et al. 2026 | five Latvian inland lakes pooled2024–2025 | median.Same samples: 30–120 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawRusko et al. 2026 | five Latvian inland lakes pooled2024–2025 | range. | ||
| Carp and other cyprinids · fresh or rawRusko et al. 2026 | five Latvian inland lakes pooled2024–2025 | median.Same samples: 40–140 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawRusko et al. 2026 | five Latvian inland lakes pooled2024–2025 | range. | ||
| Carp and other cyprinids · fresh or rawRusko et al. 2026 | five Latvian inland lakes pooled2024–2025 | median.Same samples: 55–220 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawRusko et al. 2026 | five Latvian inland lakes pooled2024–2025 | range. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Aquaculture, HungaryCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube Delta, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Carp and other cyprinids · fresh or rawTissue-Specific Mercury… 2026 | Arda River cascade reservoirs2022–2024 | median. | ||
| Carp and other cyprinids · fresh or rawTissue-Specific Mercury… 2026 | Ivaylovgrad reservoir2022–2024 | median. | ||
| Carp and other cyprinids · fresh or rawTissue-Specific Mercury… 2026 | Ivaylovgrad reservoir2022–2024 | median. | ||
| Carp and other cyprinids · fresh or rawTissue-Specific Mercury… 2026 | Arda River cascade reservoirs2022–2024 | median. | ||
| Carp and other cyprinids · fresh or rawTotal Mercury and Fatty… 2022 | Polish lakesCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawTotal Mercury and Fatty… 2022 | Polish lakesCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Carp and other cyprinids · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Carp and other cyprinids · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Carp and other cyprinids · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Carp and other cyprinids · fresh or rawVičarová et al. 2016 | Domaninský reservoir2013–2014 | mean. | ||
| Carp and other cyprinids · fresh or rawVičarová et al. 2016 | Matějovský reservoir2013–2014 | mean. | ||
| Carp and other cyprinids · fresh or rawVičarová et al. 2016 | Pilská reservoir2013–2014 | mean. | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | mean.Same samples: 100–200 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | range. | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | mean.Same samples: 230–350 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | range. | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | mean.Same samples: 120–190 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | range. | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Anzali Wetland, IranCollection date unreporteddry weight | mean.Same samples: 87–260 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Anzali Wetland, IranCollection date unreporteddry weight | range. | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | mean.Same samples: 290–400 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | range. | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | mean.Same samples: 230–460 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | range. | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Anzali Wetland, IranCollection date unreporteddry weight | mean.Same samples: 1–9 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Anzali Wetland, IranCollection date unreporteddry weight | range. | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | mean.Same samples: 120–200 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | range. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Faro, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Itaituba, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Porto TrombetasCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean.Same samples: 4.9–28.6 µg/kg (range) | ||
| Catfish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Catfish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean.Same samples: 2.9–5.6 µg/kg (range) | ||
| Catfish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Catfish · fresh or rawBrodziak-Dopierala et al. 2023 | Poland retail and direct from2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawCharacterized et al. 2025 | Amazonas region, ColombiaCollection date unreporteddry weight | sample value. | ||
| Catfish · fresh or rawCharacterized et al. 2025 | Leticia, ColombiaCollection date unreporteddry weight | sample value. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Catfish · fresh or rawEscobar-Camacho et al. 2024 | Nushiño River basin2022 | range. | ||
| Catfish · fresh or rawFuentes-Lopez et al. 2025 | San Marcos2022–2023 | mean. | ||
| Catfish · fresh or rawFuentes-Lopez et al. 2025 | San Marcos2022–2023 | mean. | ||
| Catfish · fresh or rawGerman 2024 | Germany2012–2021basis not stated | mean.Same samples: 80 µg/kg (maximum) | ||
| Catfish · fresh or rawGerman 2024 | Germany2012–2021basis not stated | max. | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: 1,600–2,720 µg/kg (range) | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: 960–3,160 µg/kg (range) | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: 630–690 µg/kg (range) | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: 870–1,490 µg/kg (range) | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: 70–110 µg/kg (range) | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: 150–720 µg/kg (range) | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean. | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean. | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: 430–950 µg/kg (range) | ||
| Catfish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Catfish · fresh or rawHealth Risk Assessment… 2023 | Atrato River, Murindo, ColombiaCollection date unreported | mean. | ||
| Catfish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | not detected. | ||
| Catfish · fresh or rawMariadi et al. 2017 | traditional marketCollection date unreportedbasis not stated | sample value. | ||
| Catfish · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreporteddry weight | mean. | ||
| Catfish · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreported | mean. | ||
| Catfish · fresh or rawMoura et al. 2022 | Jaguaribe River Estuary2015–2019basis not stated | mean. | ||
| Catfish · fresh or rawMoura et al. 2022 | Jaguaribe River Estuary2015–2019basis not stated | mean. | ||
| Catfish · fresh or rawOlmedo et al. 2013 | Vietnam2009–2010 | below LOD. | ||
| Catfish · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Catfish · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Catfish · fresh or rawPaz-Suconota et al. 2024 | Pastaza River at Santa Inés2023basis not stated | mean. | ||
| Catfish · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Catfish · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Catfish · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Catfish · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Catfish · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Catfish · fresh or rawSelenium: 2021 | Anacostia River, USA2017 | mean.Same samples: 44.2–308 µg/kg (range) | ||
| Catfish · fresh or rawSelenium: 2021 | Anacostia River, USA2017 | median. | ||
| Catfish · fresh or rawSelenium: 2021 | Anacostia River, USA2017 | range. | ||
| Catfish · fresh or rawSelenium: 2021 | Anacostia River, USA2017 | mean.Same samples: 23–284 µg/kg (range) | ||
| Catfish · fresh or rawSelenium: 2021 | Anacostia River, USA2017 | median. | ||
| Catfish · fresh or rawSelenium: 2021 | Anacostia River, USA2017 | range. | ||
| Catfish · fresh or rawSimionov et al. 2023 | Aquaculture, VietnamCollection date unreported | mean. | ||
| Catfish · fresh or rawSimionov et al. 2023 | Fishing, Danube Delta, RomaniaCollection date unreported | mean. | ||
| Catfish · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Catfish · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Catfish · fresh or rawTissue-Specific Mercury… 2026 | Arda River cascade reservoirs2022–2024 | median. | ||
| Pike · fresh or rawBrodziak-Dopierala et al. 2023 | Poland retail and direct from2021–2022basis not stated | mean. | ||
| Pike · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | mean.Same samples: 144–275 µg/kg (range) | ||
| Pike · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | median. | ||
| Pike · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | range. | ||
| Pike · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Pike · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 5,140 µg/kg (maximum) | ||
| Pike · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Pike · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Pike · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Pike · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Pike · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Pike · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Pike · fresh or rawEnvironmental 2025 | Peribonka River run-of-river2013–2019 | max. | ||
| Pike · fresh or rawEnvironmental 2025 | Saint-Maurice River run-of-river2013–2019 | mean. | ||
| Pike · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 152–849 µg/kg (range) | ||
| Pike · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean.Same samples: 408–1,760 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean.Same samples: 423–2,640 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean.Same samples: 370–1,570 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean.Same samples: 242–1,630 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean.Same samples: 44–2,030 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean.Same samples: 234–1,180 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean.Same samples: 186–1,350 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean.Same samples: 318–2,060 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean.Same samples: 397–1,500 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean.Same samples: 327–1,340 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean.Same samples: 134–826 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean.Same samples: 292–2,000 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean.Same samples: 342–1,310 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean.Same samples: 195–1,450 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 130–1,430 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | not detected. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 213–647 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 1–37 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 346–999 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 14–84 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 325–2,160 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: up to 208 µg/kg (range maximum) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 307–828 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 102–236 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 484–755 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 147–286 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 257–1,360 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 117–514 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 338–1,280 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 29–480 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 380–1,580 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 133–642 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 279–1,180 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 31–454 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 212–1,720 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 34–633 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 102–1,120 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 26–323 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 298–1,900 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 32–494 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 255–1,660 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 17–445 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 530–1,510 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean.Same samples: 40–390 µg/kg (range) | ||
| Pike · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | range. | ||
| Pike · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | mean.Same samples: 71–287 µg/kg (range) | ||
| Pike · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | range. | ||
| Pike · fresh or rawMajlesi et al. 2017 | Khersan River2016basis not stated | mean. | ||
| Pike · fresh or rawMercury in Selected… 2023 | Lake Insko, north-western PolandCollection date unreported | mean.Same samples: 3–22 µg/kg (range) | ||
| Pike · fresh or rawMercury in Selected… 2023 | Lake Insko, north-western PolandCollection date unreported | range. | ||
| Pike · fresh or rawMercury in Selected… 2023 | Lake Wisola, north-western PolandCollection date unreported | mean.Same samples: 2–214 µg/kg (range) | ||
| Pike · fresh or rawMercury in Selected… 2023 | Lake Wisola, north-western PolandCollection date unreported | range. | ||
| Pike · fresh or rawRusko et al. 2026 | five Latvian inland lakes pooled2024–2025 | median.Same samples: 100–1,110 µg/kg (range) | ||
| Pike · fresh or rawRusko et al. 2026 | five Latvian inland lakes pooled2024–2025 | range. | ||
| Pike · fresh or rawtotal mercury (THg),… 2026 | Lake Vanajanselka, Finland1970–2002 | median.Same samples: 50–390 µg/kg (range) | ||
| Pike · fresh or rawtotal mercury (THg),… 2026 | Lake Vanajanselka, Finland1970–2002 | range. | ||
| Pike · fresh or rawtotal mercury (THg),… 2026 | Northern Quark1970–2002 | median.Same samples: 80–1,220 µg/kg (range) | ||
| Pike · fresh or rawtotal mercury (THg),… 2026 | Northern Quark1970–2002 | range. | ||
| Pike · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Pike · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Perch, walleye and zander · fresh or rawASSESSING HUMAN RISKS… 2024 | reservoirCollection date unreported | mean. | ||
| Perch, walleye and zander · fresh or rawBrodziak-Dopierala et al. 2023 | Poland retail and direct from2021–2022basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawComputational… 2024 | Bad River, Wisconsin2017–2021 | mean. | ||
| Perch, walleye and zander · fresh or rawComputational… 2024 | St. Louis River AOC2017–2021 | mean. | ||
| Perch, walleye and zander · fresh or rawComputational… 2024 | St. Louis River AOC2017–2021 | mean. | ||
| Perch, walleye and zander · fresh or rawComputational… 2024 | St. Louis River AOC2017–2021 | mean. | ||
| Perch, walleye and zander · fresh or rawComputational… 2024 | St. Louis River AOC2017–2021 | mean. | ||
| Perch, walleye and zander · fresh or rawComputational… 2024 | St. Louis River AOC2017–2021 | mean. | ||
| Perch, walleye and zander · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | mean.Same samples: 110–282 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | median. | ||
| Perch, walleye and zander · fresh or rawConcentration of… 2016 | Lake Pluszne, PolandCollection date unreported | range. | ||
| Perch, walleye and zander · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | mean. | ||
| Perch, walleye and zander · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | max. | ||
| Perch, walleye and zander · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Perch, walleye and zander · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 780 µg/kg (maximum) | ||
| Perch, walleye and zander · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Perch, walleye and zander · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Perch, walleye and zander · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Perch, walleye and zander · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Perch, walleye and zander · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Perch, walleye and zander · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Perch, walleye and zander · fresh or rawEnvironmental 2025 | Saint-Maurice River run-of-river2013–2019 | mean. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 78–1,350 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 114–245 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 57–369 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 2402001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawHttps://doi.org/./s---… 2021 | Lake 6582001–2015 | mean. | ||
| Perch, walleye and zander · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | mean.Same samples: 71–254 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | range. | ||
| Perch, walleye and zander · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawmethylmercury burdens… 2009 | Athabasca River, Alberta, Canada2014–2016dry weight | mean.Same samples: 700–5,220 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawmethylmercury burdens… 2009 | Athabasca River, Alberta, Canada2014–2016dry weight | range. | ||
| Perch, walleye and zander · fresh or rawmethylmercury burdens… 2009 | Lake Athabasca, Alberta, Canada2014–2016dry weight | mean.Same samples: 610–4,760 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawmethylmercury burdens… 2009 | Lake Athabasca, Alberta, Canada2014–2016dry weight | range. | ||
| Perch, walleye and zander · fresh or rawRusko et al. 2026 | five Latvian inland lakes pooled2024–2025 | median.Same samples: 70–525 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawRusko et al. 2026 | five Latvian inland lakes pooled2024–2025 | range. | ||
| Perch, walleye and zander · fresh or rawRusko et al. 2026 | five Latvian inland lakes pooled2024–2025 | median.Same samples: 10–740 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawRusko et al. 2026 | five Latvian inland lakes pooled2024–2025 | range. | ||
| Perch, walleye and zander · fresh or rawSelenium: 2021 | Lake Erie, Great Lakes, USA2017 | mean.Same samples: 86.7–649 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawSelenium: 2021 | Lake Erie, Great Lakes, USA2017 | median. | ||
| Perch, walleye and zander · fresh or rawSelenium: 2021 | Lake Erie, Great Lakes, USA2017 | range. | ||
| Perch, walleye and zander · fresh or rawSelenium: 2021 | Lake Erie, Great Lakes, USA2017 | mean.Same samples: 87.5–556 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawSelenium: 2021 | Lake Erie, Great Lakes, USA2017 | median. | ||
| Perch, walleye and zander · fresh or rawSelenium: 2021 | Lake Erie, Great Lakes, USA2017 | range. | ||
| Perch, walleye and zander · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Perch, walleye and zander · fresh or rawTissue-Specific Mercury… 2026 | Arda River cascade reservoirs2022–2024 | median. | ||
| Perch, walleye and zander · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Perch, walleye and zander · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Perch, walleye and zander · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021dry weight | mean. | ||
| Perch, walleye and zander · fresh or rawVainio et al. 2022 | Archipelago Sea2013–2021 | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | Valdeazogues River transectCollection date unreporteddry weight | mean.Same samples: 1,660–24,500 µg/kg (range); 473–7,610 µg/kg (range) | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | Valdeazogues River transectCollection date unreported | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | Valdeazogues River transectCollection date unreporteddry weight | range. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | Valdeazogues River transectCollection date unreported | range. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | Castilseras reservoirCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | Castilseras reservoirCollection date unreported | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | El Entredicho open pit lakeCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | El Entredicho open pit lakeCollection date unreported | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | La Colada reservoirCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | La Colada reservoirCollection date unreported | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PLPCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PLPCollection date unreported | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PPACollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PPACollection date unreported | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PPMCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PPMCollection date unreported | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PTHCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PTHCollection date unreported | mean. | ||
| Black bass and sunfish · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Black bass and sunfish · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Black bass and sunfish · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | mean.Same samples: 78–140 µg/kg (range) | ||
| Black bass and sunfish · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | range. | ||
| Black bass and sunfish · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | mean.Same samples: 56–161 µg/kg (range) | ||
| Black bass and sunfish · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | range. | ||
| Black bass and sunfish · fresh or rawPáez-Osuna et al. 2024 | El Comedero dam2013–2014 | mean.Same samples: 70–560 µg/kg (range) | ||
| Black bass and sunfish · fresh or rawPáez-Osuna et al. 2024 | El Comedero dam2013–2014 | range. | ||
| Black bass and sunfish · fresh or rawPáez-Osuna et al. 2024 | El Comedero dam2013–2014dry weight | mean. | ||
| Black bass and sunfish · fresh or rawSelenium: 2021 | Potomac River, USA2017 | mean.Same samples: 74–526 µg/kg (range) | ||
| Black bass and sunfish · fresh or rawSelenium: 2021 | Potomac River, USA2017 | median. | ||
| Black bass and sunfish · fresh or rawSelenium: 2021 | Potomac River, USA2017 | range. | ||
| Black bass and sunfish · fresh or rawSelenium: 2021 | Potomac River, USA2017 | mean.Same samples: 86.8–475 µg/kg (range) | ||
| Black bass and sunfish · fresh or rawSelenium: 2021 | Potomac River, USA2017 | median. | ||
| Black bass and sunfish · fresh or rawSelenium: 2021 | Potomac River, USA2017 | range. | ||
| Black bass and sunfish · fresh or rawSelenium: 2021 | St. Lawrence River, USA2017 | mean.Same samples: 99.6–322 µg/kg (range) | ||
| Black bass and sunfish · fresh or rawSelenium: 2021 | St. Lawrence River, USA2017 | median. | ||
| Black bass and sunfish · fresh or rawSelenium: 2021 | St. Lawrence River, USA2017 | range. | ||
| Black bass and sunfish · fresh or rawSelenium: 2021 | St. Lawrence River, USA2017 | mean.Same samples: 105–317 µg/kg (range) | ||
| Black bass and sunfish · fresh or rawSelenium: 2021 | St. Lawrence River, USA2017 | median. | ||
| Black bass and sunfish · fresh or rawSelenium: 2021 | St. Lawrence River, USA2017 | range. | ||
| Black bass and sunfish · fresh or rawSimionov et al. 2023 | Aquaculture, ItalyCollection date unreported | mean. | ||
| Black bass and sunfish · fresh or rawWillacker et al. 2023 | Snake River, USA, electrofished2013–2020 | geometric mean.Same samples: 7–1,470 µg/kg (range) | ||
| Black bass and sunfish · fresh or rawWillacker et al. 2023 | Snake River, USA, electrofished2013–2020 | range. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Faro, western Pará, BrazilCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Itaituba, western Pará, BrazilCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Porto TrombetasCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean.Same samples: 6.1–29.4 µg/kg (range) | ||
| Other cichlids · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Other cichlids · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean.Same samples: 3.3–22.7 µg/kg (range) | ||
| Other cichlids · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Other cichlids · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean.Same samples: 4.2–12.9 µg/kg (range) | ||
| Other cichlids · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Other cichlids · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean.Same samples: 13.3–59.5 µg/kg (range) | ||
| Other cichlids · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Other cichlids · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: 170–650 µg/kg (range) | ||
| Other cichlids · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Other cichlids · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: 490–1,120 µg/kg (range) | ||
| Other cichlids · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Other cichlids · fresh or rawHealth Risk Assessment… 2023 | Atrato River, Murindo, ColombiaCollection date unreported | mean. | ||
| Other cichlids · fresh or rawOliveira et al. 2022 | Small lakes around São Luiz do2018–2019 | mean.Same samples: 170–1,680 µg/kg (range) | ||
| Other cichlids · fresh or rawOliveira et al. 2022 | Small lakes around São Luiz do2018–2019 | median. | ||
| Other cichlids · fresh or rawOliveira et al. 2022 | Small lakes around São Luiz do2018–2019 | range. | ||
| Other cichlids · fresh or rawOliveira et al. 2022 | Small lakes around São Luiz do2018–2019 | mean.Same samples: 120–940 µg/kg (range) | ||
| Other cichlids · fresh or rawOliveira et al. 2022 | Small lakes around São Luiz do2018–2019 | median. | ||
| Other cichlids · fresh or rawOliveira et al. 2022 | Small lakes around São Luiz do2018–2019 | range. | ||
| Other cichlids · fresh or rawPaz-Suconota et al. 2024 | Pastaza River at Santa Inés2023basis not stated | mean. | ||
| Other cichlids · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Snakehead · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Faro, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Itaituba, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean.Same samples: 3.2–8.4 µg/kg (range) | ||
| Other freshwater fish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Other freshwater fish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean. | ||
| Other freshwater fish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Other freshwater fish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean.Same samples: 5.7–21.6 µg/kg (range) | ||
| Other freshwater fish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Other freshwater fish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean.Same samples: 12.6–49.5 µg/kg (range) | ||
| Other freshwater fish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Other freshwater fish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean.Same samples: 3–27.1 µg/kg (range) | ||
| Other freshwater fish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Other freshwater fish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean.Same samples: 7.6–68.5 µg/kg (range) | ||
| Other freshwater fish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Other freshwater fish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | mean.Same samples: 5.2–7.7 µg/kg (range) | ||
| Other freshwater fish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | range. | ||
| Other freshwater fish · fresh or rawAquaculture 2026 | Jaguaribe basin2013–2023 | sample value. | ||
| Other freshwater fish · fresh or rawBrodziak-Dopierala et al. 2023 | Poland retail and direct from2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | geometric mean.Same samples: 70–2,400 µg/kg (range) | ||
| Other freshwater fish · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | range. | ||
| Other freshwater fish · fresh or rawChristian et al. 2024 | Suriname2005–2023 | geometric mean.Same samples: 120–780 µg/kg (range) | ||
| Other freshwater fish · fresh or rawChristian et al. 2024 | Suriname2005–2023 | range. | ||
| Other freshwater fish · fresh or rawChristian et al. 2024 | Suriname2005–2023 | geometric mean.Same samples: 70–2,400 µg/kg (range) | ||
| Other freshwater fish · fresh or rawChristian et al. 2024 | Suriname2005–2023 | range. | ||
| Other freshwater fish · fresh or rawcontrasting levels of… 2025 | Abeek, Flanders, Belgium2017dry weight | median. | ||
| Other freshwater fish · fresh or rawcontrasting levels of… 2025 | 21 Flemish sites2017dry weight | range. | ||
| Other freshwater fish · fresh or rawcontrasting levels of… 2025 | Laakbeek, Flanders, Belgium2017dry weight | median. | ||
| Other freshwater fish · fresh or rawcontrasting levels of… 2025 | Lede, Flanders, Belgium2017dry weight | median. | ||
| Other freshwater fish · fresh or rawcontrasting levels of… 2025 | Molenaarsdreefbeek2017dry weight | median. | ||
| Other freshwater fish · fresh or rawcontrasting levels of… 2025 | Molenbeek, Flanders, Belgium2017dry weight | median. | ||
| Other freshwater fish · fresh or rawcontrasting levels of… 2025 | Mombeek, Flanders, Belgium2017dry weight | median. | ||
| Other freshwater fish · fresh or rawcontrasting levels of… 2025 | Motebeek, Flanders, Belgium2017dry weight | median. | ||
| Other freshwater fish · fresh or rawcontrasting levels of… 2025 | Velpe, Flanders, Belgium2017dry weight | median. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Other freshwater fish · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Other freshwater fish · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Other freshwater fish · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Other freshwater fish · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Other freshwater fish · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Other freshwater fish · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 19–349 µg/kg (range) | ||
| Other freshwater fish · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Other freshwater fish · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Other freshwater fish · fresh or rawFuentes-Lopez et al. 2025 | San Marcos2022–2023 | mean. | ||
| Other freshwater fish · fresh or rawFuentes-Lopez et al. 2025 | San Marcos2022–2023 | mean. | ||
| Other freshwater fish · fresh or rawFuentes-Lopez et al. 2025 | San Marcos2022–2023 | mean. | ||
| Other freshwater fish · fresh or rawFuentes-Lopez et al. 2025 | San Marcos2022–2023 | mean. | ||
| Other freshwater fish · fresh or rawFuentes-Lopez et al. 2025 | San Marcos2022–2023 | mean. | ||
| Other freshwater fish · fresh or rawFuentes-Lopez et al. 2025 | San Marcos2022–2023 | mean. | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: 10–280 µg/kg (range) | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: 70–110 µg/kg (range) | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: 40–40 µg/kg (range) | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: 70–200 µg/kg (range) | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: up to 70 µg/kg (range maximum) | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean. | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean.Same samples: 380–420 µg/kg (range) | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2023 | Atrato RiverCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Other freshwater fish · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | mean.Same samples: 361–880 µg/kg (range) | ||
| Other freshwater fish · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | range. | ||
| Other freshwater fish · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | mean.Same samples: 387–1,040 µg/kg (range) | ||
| Other freshwater fish · fresh or rawMelnyk et al. 2021 | Penobscot River, Maine, USA2017–2018 | range. | ||
| Other freshwater fish · fresh or rawMelnyk et al. 2021 | Penobscot River and estuary2017–2018 | mean. | ||
| Other freshwater fish · fresh or rawOlmedo et al. 2013 | Tanzania2009–2010 | median. | ||
| Other freshwater fish · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Other freshwater fish · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Other freshwater fish · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Other freshwater fish · fresh or rawPaz-Suconota et al. 2024 | Pastaza River at Santa Inés2023basis not stated | mean. | ||
| Other freshwater fish · fresh or rawPaz-Suconota et al. 2024 | Pastaza River at Santa Inés2023basis not stated | mean. | ||
| Other freshwater fish · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Other freshwater fish · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Other freshwater fish · fresh or rawPaz-Suconota et al. 2024 | Pastaza River at Santa Inés2023basis not stated | mean. | ||
| Other freshwater fish · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Other freshwater fish · fresh or rawPaz-Suconota et al. 2024 | Pastaza River at Santa Inés2023basis not stated | mean. | ||
| Other freshwater fish · fresh or rawRundio et al. 2022 | Big Creek2005–2020dry weight | geometric mean. | ||
| Other freshwater fish · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | mean.Same samples: 30–3,270 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | range. | ||
| Marine fish, species not stated · fresh or rawassessed the risks and… 2026 | commercially available foodsCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawBlanco et al. 2023 | various2011–2017basis not stated | mean.Same samples: 100–1,200 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawBlanco et al. 2023 | various2011–2017basis not stated | median. | ||
| Marine fish, species not stated · fresh or rawBlanco et al. 2023 | various2011–2017basis not stated | range. | ||
| Marine fish, species not stated · fresh or rawBlanco et al. 2023 | various2011–2017basis not stated | median. | ||
| Marine fish, species not stated · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | geometric mean.Same samples: up to 5,710 µg/kg (range maximum) | ||
| Marine fish, species not stated · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | range. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | mean. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | median. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | range. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | mean. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | median. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | range. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | mean. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | median. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | range. | ||
| Marine fish, species not stated · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Marine fish, species not stated · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Marine fish, species not stated · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | range. | ||
| Marine fish, species not stated · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | range. | ||
| Marine fish, species not stated · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | range. | ||
| Marine fish, species not stated · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Marine fish, species not stated · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Marine fish, species not stated · fresh or rawDinesh et al. 2025 | Bay of BengalCollection date unreportedbasis not stated | below LOD. | ||
| Marine fish, species not stated · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 4–272 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Marine fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 1,000 µg/kg (maximum) | ||
| Marine fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Marine fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Marine fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Marine fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Marine fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Marine fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Marine fish, species not stated · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 40–40 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Marine fish, species not stated · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Marine fish, species not stated · fresh or rawEuropean et al. 2004 | Italy national submission to SCOOP1990–2002basis not stated | mean. | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | mean.Same samples: 13,000 µg/kg (maximum) | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | median. | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | max. | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | range. | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | mean.Same samples: 1,820 µg/kg (maximum) | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | median. | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | max. | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | mean.Same samples: 13,000 µg/kg (maximum) | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | median. | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | max. | ||
| Marine fish, species not stated · fresh or rawGladys et al. 2026 | Central Market of Lima2023 | mean.Same samples: 8–358 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawGladys et al. 2026 | Central Market of Lima2023 | range. | ||
| Marine fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | mean.Same samples: 3–2,250 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | range. | ||
| Marine fish, species not stated · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean. | ||
| Marine fish, species not stated · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean.Same samples: up to 780 µg/kg (range maximum) | ||
| Marine fish, species not stated · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | range. | ||
| Marine fish, species not stated · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean.Same samples: 30–3,160 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | range. | ||
| Marine fish, species not stated · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | sample value. | ||
| Marine fish, species not stated · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Marine fish, species not stated · fresh or rawSuzuki et al. 2022 | not stated in primary2019–2020basis not stated | mean. | ||
| Marine fish, species not stated · fresh or rawSuzuki et al. 2022 | not stated in primary2019–2020basis not stated | mean. | ||
| Marine fish, species not stated · fresh or rawSuzuki et al. 2022 | not stated in primary2019–2020basis not stated | mean. | ||
| Marine fish, species not stated · fresh or rawSuzuki et al. 2022 | not stated in primary2019–2020basis not stated | mean. | ||
| Marine fish, species not stated · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | not detected. | ||
| Freshwater fish, species not stated · fresh or rawA Novel Approach to… 2025 | Lake Puruzinho, Amazonas, Brazil2019–2020 | mean. | ||
| Freshwater fish, species not stated · fresh or rawA Novel Approach to… 2025 | Lake Puruzinho, Amazonas, Brazil2019–2020 | mean. | ||
| Freshwater fish, species not stated · fresh or rawA Novel Approach to… 2025 | Lake Puruzinho, Amazonas, Brazil2019–2020 | mean. | ||
| Freshwater fish, species not stated · fresh or rawA Novel Approach to… 2025 | Lake Puruzinho, Amazonas, Brazil2019–2020 | mean. | ||
| Freshwater fish, species not stated · fresh or rawA Novel Approach to… 2025 | Lake Puruzinho, Amazonas, Brazil2019–2020 | mean. | ||
| Freshwater fish, species not stated · fresh or rawassessed the risks and… 2026 | commercially available foodsCollection date unreported | mean. | ||
| Freshwater fish, species not stated · fresh or rawChristian et al. 2024 | Suriname2005–2023 | geometric mean.Same samples: 20–2,400 µg/kg (range) | ||
| Freshwater fish, species not stated · fresh or rawChristian et al. 2024 | Suriname2005–2023 | range. | ||
| Freshwater fish, species not stated · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | geometric mean.Same samples: 10–3,720 µg/kg (range) | ||
| Freshwater fish, species not stated · fresh or rawChristian et al. 2024 | wider Caribbean Region2005–2023 | range. | ||
| Freshwater fish, species not stated · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | geometric mean.Same samples: 1–28,500 µg/kg (range) | ||
| Freshwater fish, species not stated · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | range. | ||
| Freshwater fish, species not stated · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | range. | ||
| Freshwater fish, species not stated · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | range. | ||
| Freshwater fish, species not stated · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | mean. | ||
| Freshwater fish, species not stated · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | mean. | ||
| Freshwater fish, species not stated · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | mean. | ||
| Freshwater fish, species not stated · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | mean. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Aguarico River basin2022 | mean. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Nushiño River basin2022 | mean. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Napo River basin2022 | range. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Nushiño River basin2022 | mean. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Aguarico River basin2022 | mean. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Nushiño River basin2022 | range. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Aguarico River basin2022 | range. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Nushiño River basin2022 | mean. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Nushiño River basin2022 | range. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Nushiño River basin2022 | mean. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Nushiño River basin2022 | range. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Nushiño River basin2022 | mean. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Aguarico River basin2022 | mean. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Nushiño River basin2022 | range. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Aguarico River basin2022 | range. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Nushiño River basin2022 | mean. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Aguarico River basin2022 | mean. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Nushiño River basin2022 | range. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Aguarico River basin2022 | range. | ||
| Freshwater fish, species not stated · fresh or rawEscobar-Camacho et al. 2024 | Aguarico River basin2022 | sample value. | ||
| Freshwater fish, species not stated · fresh or rawFuentes-Lopez et al. 2025 | San Marcos2022–2023 | mean.Same samples: 10–850 µg/kg (range) | ||
| Freshwater fish, species not stated · fresh or rawFuentes-Lopez et al. 2025 | San Marcos2022–2023 | range. | ||
| Freshwater fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | mean.Same samples: 650 µg/kg (maximum) | ||
| Freshwater fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | median. | ||
| Freshwater fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | max. | ||
| Freshwater fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean. | ||
| Freshwater fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Lower Branco River2021 | mean. | ||
| Freshwater fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Lower Branco River2021 | median. | ||
| Freshwater fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Lower Mucajaí River2021 | mean. | ||
| Freshwater fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Lower Mucajaí River2021 | median. | ||
| Freshwater fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Branco River at Boa Vista2021 | mean. | ||
| Freshwater fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Branco River at Boa Vista2021 | median. | ||
| Freshwater fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Uraricoera River, Roraima, Brazil2021 | mean. | ||
| Freshwater fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Uraricoera River, Roraima, Brazil2021 | median. | ||
| Freshwater fish, species not stated · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Freshwater fish, species not stated · fresh or rawPaz-Suconota et al. 2024 | Pastaza River at Santa Inés2023basis not stated | mean. | ||
| Freshwater fish, species not stated · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Freshwater fish, species not stated · fresh or rawPaz-Suconota et al. 2024 | Pastaza River at Santa Inés2023basis not stated | mean. | ||
| Freshwater fish, species not stated · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Freshwater fish, species not stated · fresh or rawPaz-Suconota et al. 2024 | Pastaza River at Santa Inés2023basis not stated | mean. | ||
| Freshwater fish, species not stated · fresh or rawPaz-Suconota et al. 2024 | Metzeras River2023basis not stated | mean. | ||
| Freshwater fish, species not stated · fresh or rawPaz-Suconota et al. 2024 | Pastaza River at Santa Inés2023basis not stated | mean. | ||
| Freshwater fish, species not stated · fresh or rawStahl et al. 2023 | random river sites >=5th order2013–2018 | mean.Same samples: 8.61 µg/kg (minimum); 1,070 µg/kg (maximum) | ||
| Freshwater fish, species not stated · fresh or rawStahl et al. 2023 | random river sites >=5th order2013–2018 | median. | ||
| Freshwater fish, species not stated · fresh or rawStahl et al. 2023 | random river sites >=5th order2013–2018 | min. | ||
| Freshwater fish, species not stated · fresh or rawStahl et al. 2023 | random river sites >=5th order2013–2018 | max. | ||
| Freshwater fish, species not stated · fresh or rawStahl et al. 2023 | random river sites >=5th order2013–2018 | mean.Same samples: 9.44 µg/kg (minimum); 1,340 µg/kg (maximum) | ||
| Freshwater fish, species not stated · fresh or rawStahl et al. 2023 | random river sites >=5th order2013–2018 | median. | ||
| Freshwater fish, species not stated · fresh or rawStahl et al. 2023 | random river sites >=5th order2013–2018 | min. | ||
| Freshwater fish, species not stated · fresh or rawStahl et al. 2023 | random river sites >=5th order2013–2018 | max. | ||
| Freshwater fish, species not stated · fresh or rawTissue-Specific Mercury… 2026 | Arda River cascade reservoirs2022–2024 | mean.Same samples: 8–116 µg/kg (range) | ||
| Freshwater fish, species not stated · fresh or rawTissue-Specific Mercury… 2026 | Arda River cascade reservoirs2022–2024 | median. | ||
| Freshwater fish, species not stated · fresh or rawTissue-Specific Mercury… 2026 | Arda River cascade reservoirs2022–2024 | range. | ||
| Freshwater fish, species not stated · fresh or rawTissue-Specific Mercury… 2026 | Ivaylovgrad reservoir2022–2024 | mean. | ||
| Freshwater fish, species not stated · fresh or rawTissue-Specific Mercury… 2026 | Kardzhali reservoir2022–2024 | mean. | ||
| Freshwater fish, species not stated · fresh or rawTissue-Specific Mercury… 2026 | Studen Kladenets reservoir2022–2024 | mean. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2004–2020 | median. | ||
| Fish, species not stated · fresh or rawAl-Sulaiti et al. 2023 | Local and imported2021–2022dry weight | mean. | ||
| Fish, species not stated · fresh or rawAl-Sulaiti et al. 2023 | Local and imported2021–2022 | mean. | ||
| Fish, species not stated · fresh or rawassessed the risks and… 2026 | commercially available foodsCollection date unreported | mean. | ||
| Fish, species not stated · fresh or rawBlanco et al. 2023 | various2011–2017basis not stated | mean.Same samples: 10–1,310 µg/kg (range) | ||
| Fish, species not stated · fresh or rawBlanco et al. 2023 | various2011–2017basis not stated | median. | ||
| Fish, species not stated · fresh or rawBlanco et al. 2023 | various2011–2017basis not stated | range. | ||
| Fish, species not stated · fresh or rawBrodziak-Dopierala et al. 2023 | Poland retail and direct from2021–2022basis not stated | mean.Same samples: 4–827 µg/kg (range) | ||
| Fish, species not stated · fresh or rawBrodziak-Dopierala et al. 2023 | Poland retail and direct from2021–2022basis not stated | median. | ||
| Fish, species not stated · fresh or rawBrodziak-Dopierala et al. 2023 | Poland retail and direct from2021–2022basis not stated | range. | ||
| Fish, species not stated · fresh or rawBrodziak-Dopierala et al. 2023 | Poland retail and direct from2021–2022basis not stated | mean. | ||
| Fish, species not stated · fresh or rawBrodziak-Dopierala et al. 2023 | Poland retail and direct from2021–2022basis not stated | mean. | ||
| Fish, species not stated · fresh or rawBrodziak-Dopierala et al. 2023 | Poland retail and direct from2021–2022basis not stated | mean. | ||
| Fish, species not stated · fresh or rawBrodziak-Dopierala et al. 2023 | Poland retail and direct from2021–2022basis not stated | median. | ||
| Fish, species not stated · fresh or rawBrodziak-Dopierala et al. 2023 | Poland retail and direct from2021–2022basis not stated | mean. | ||
| Fish, species not stated · fresh or rawBrodziak-Dopierala et al. 2023 | Poland retail and direct from2021–2022basis not stated | median. | ||
| Fish, species not stated · fresh or rawChen et al. 2025 | Chongqing retail outlets2017–2021basis not stated | mean. | ||
| Fish, species not stated · fresh or rawChen et al. 2025 | Chongqing retail outlets2017–2021basis not stated | mean. | ||
| Fish, species not stated · fresh or rawChen et al. 2025 | Chongqing retail outlets2017–2021basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEagles-Smith et al. 2016 | Western United States and Canada1969–2014 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 6,890 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 6,760 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 6,890 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 950 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | France national submission to1990–2002basis not stated | mean.Same samples: up to 4,300 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | France national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Belgium national submission to1990–2002basis not stated | mean.Same samples: up to 2,120 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Belgium national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Denmark national submission to1990–2002basis not stated | mean.Same samples: 11–201 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Denmark national submission to1990–2002basis not stated | median. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Denmark national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | France national submission to1990–2002basis not stated | mean.Same samples: up to 857 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | France national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Germany national submission to1990–2002basis not stated | mean.Same samples: up to 5,800 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Germany national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 25–823 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: up to 3,700 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Norway national submission to1990–2002basis not stated | mean.Same samples: 24–3,980 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Norway national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Norway national submission to1990–2002basis not stated | mean.Same samples: 4–260 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Norway national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Portugal national submission to1990–2002basis not stated | mean.Same samples: 10–1,660 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Portugal national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Sweden national submission to1990–2002basis not stated | mean.Same samples: 10–2,200 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Sweden national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | mean.Same samples: 17–92 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | mean.Same samples: 16–240 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 10–340 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–420 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 200–560 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 35–205 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawFood 2016 | UK retail2013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawFood et al. 2014 | UK retail outlets, 2013-20142013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | range. | ||
| Fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean. | ||
| Fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean. | ||
| Fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean. | ||
| Fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | median. | ||
| Fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean. | ||
| Fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | median. | ||
| Fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean. | ||
| Fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | median. | ||
| Fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean. | ||
| Fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | mean. | ||
| Fish, species not stated · fresh or rawHealth Risk Assessment… 2022 | Branco River Basin2021 | median. | ||
| Fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | mean.Same samples: 4–236 µg/kg (range) | ||
| Fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | range. | ||
| Fish, species not stated · fresh or rawLim et al. 2015 | Supermarkets and marketplaces in2010–2011basis not stated | mean.Same samples: 9.4–5,270 µg/kg (range) | ||
| Fish, species not stated · fresh or rawLim et al. 2015 | Supermarkets and marketplaces in2010–2011basis not stated | median. | ||
| Fish, species not stated · fresh or rawLim et al. 2015 | Supermarkets and marketplaces in2010–2011basis not stated | range. | ||
| Fish, species not stated · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | mean.Same samples: up to 350 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawLin et al. 2021 | Fishing portsCollection date unreportedbasis not stated | range. | ||
| Fish, species not stated · fresh or rawOlmedo et al. 2013 | Granada, Spain2009–2010 | median. | ||
| Fish, species not stated · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Fish, species not stated · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Fish, species not stated · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Fish, species not stated · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Fish, species not stated · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Fish, species not stated · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Fish, species not stated · fresh or rawSeafood 2022 | Peninsular Malaysia2009dry weight | median. | ||
| Fish, species not stated · fresh or rawSeafood 2022 | Peninsular Malaysia2009 | median. | ||
| Fish, species not stated · fresh or rawSelenium: 2021 | Great Lakes and Anacostia2017 | mean.Same samples: 44.2–649 µg/kg (range) | ||
| Fish, species not stated · fresh or rawSelenium: 2021 | Great Lakes and Anacostia2017 | median. | ||
| Fish, species not stated · fresh or rawSelenium: 2021 | Great Lakes and Anacostia2017 | range. | ||
| Fish, species not stated · fresh or rawSelenium: 2021 | Great Lakes and Anacostia2017 | mean.Same samples: 23–556 µg/kg (range) | ||
| Fish, species not stated · fresh or rawSelenium: 2021 | Great Lakes and Anacostia2017 | median. | ||
| Fish, species not stated · fresh or rawSelenium: 2021 | Great Lakes and Anacostia2017 | range. | ||
| Fish, species not stated · fresh or rawSuzuki et al. 2022 | not stated in primary2019–2020basis not stated | mean. | ||
36 findings · 6 studies · 9 spread figures folded in | ||||
| Tuna · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Tuna · smoked, dried, salted or fermentedFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Tuna · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Shark · smoked, dried, salted or fermentedFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Shark · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Mackerel · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 30–90 µg/kg (range) | ||
| Mackerel · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Herring · smoked, dried, salted or fermentedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 37–63 µg/kg (range) | ||
| Herring · smoked, dried, salted or fermentedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Herring · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Herring · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 20–60 µg/kg (range) | ||
| Herring · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Herring · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Herring · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 10–80 µg/kg (range) | ||
| Herring · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Herring · smoked, dried, salted or fermentedFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Herring · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Herring · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Herring · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Herring · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Herring · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | not detected. | ||
| Sardine and pilchard · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | mean. | ||
| Sprat · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Salmon · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 20–50 µg/kg (range) | ||
| Salmon · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Salmon · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Trout and char · smoked, dried, salted or fermentedGerman 2024 | Germany, Eastern region2012–2021basis not stated | mean. | ||
| Trout and char · smoked, dried, salted or fermentedGerman 2024 | Germany, Northern region2012–2021basis not stated | mean. | ||
| Trout and char · smoked, dried, salted or fermentedGerman 2024 | Germany, Southern region2012–2021basis not stated | mean. | ||
| Trout and char · smoked, dried, salted or fermentedGerman 2024 | Germany, Western region2012–2021basis not stated | mean. | ||
| Haddock · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 100–180 µg/kg (range) | ||
| Haddock · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Pollock and saithe · smoked, dried, salted or fermentedDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 12–44 µg/kg (range) | ||
| Pollock and saithe · smoked, dried, salted or fermentedDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Halibut · smoked, dried, salted or fermentedFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Halibut · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Grey mullet · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | mean. | ||
| Grey mullet · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | mean. | ||
| Eel · smoked, dried, salted or fermentedFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Eel · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBrima et al. 2025 | various African countries2023–2024dry weight | mean.Same samples: 100–300 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBrima et al. 2025 | various African countries2023–2024dry weight | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: up to 545 µg/kg (range maximum) | ||
| Fish, species not stated · smoked, dried, salted or fermentedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
16 findings · 4 studies · 2 spread figures folded in | ||||
| Shark · fish oilBrodziak-Dopierała et al. 2023 | Poland: pharmaciesCollection date unreportedbasis not stated | mean. | ||
| Shark · fish oilBrodziak-Dopierała et al. 2023 | Poland: pharmaciesCollection date unreportedbasis not stated | median. | ||
| Shark · fish oilBrodziak-Dopierała et al. 2023 | Poland: pharmaciesCollection date unreportedbasis not stated | range. | ||
| Cod · fish oilWHO GEMS/Food | WHO region EURO2004–2015 | median. | ||
| Cod · fish oilBrodziak-Dopierała et al. 2023 | Poland: pharmaciesCollection date unreportedbasis not stated | mean. | ||
| Cod · fish oilBrodziak-Dopierała et al. 2023 | Poland: pharmaciesCollection date unreportedbasis not stated | median. | ||
| Cod · fish oilBrodziak-Dopierała et al. 2023 | Poland: pharmaciesCollection date unreportedbasis not stated | range. | ||
| Marine fish, species not stated · fish oilBrodziak-Dopierała et al. 2023 | Poland: pharmaciesCollection date unreportedbasis not stated | median. | ||
| Fish, species not stated · fish oilWHO GEMS/Food | WHO region EURO2004–2018 | median. | ||
| Fish, species not stated · fish oilEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 100 µg/kg (maximum) | ||
| Fish, species not stated · fish oilEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fish oilEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fish oilEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fish oilEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fish oilEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fish oilEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Fish, species not stated · fish oilTorović et al. 2024 | markets of the Republic of SerbiaCollection date unreportedbasis not stated | mean.Same samples: 1–5.7 µg/kg (range) | ||
| Fish, species not stated · fish oilTorović et al. 2024 | markets of the Republic of SerbiaCollection date unreportedbasis not stated | range. | ||
11 findings · 1 study · 1 spread figure folded in | ||||
| Anchovy · fish sauceDiviš et al. 2020 | Vietnam, ThailandCollection date unreportedbasis not stated | mean.Same samples: 0.8–42.8 µg/kg (range) | ||
| Anchovy · fish sauceDiviš et al. 2020 | Vietnam, ThailandCollection date unreportedbasis not stated | range. | ||
| Anchovy · fish sauceDiviš et al. 2020 | VietnamCollection date unreportedbasis not stated | sample value. | ||
| Anchovy · fish sauceDiviš et al. 2020 | ThailandCollection date unreportedbasis not stated | sample value. | ||
| Anchovy · fish sauceDiviš et al. 2020 | VietnamCollection date unreportedbasis not stated | sample value. | ||
| Anchovy · fish sauceDiviš et al. 2020 | VietnamCollection date unreportedbasis not stated | sample value. | ||
| Anchovy · fish sauceDiviš et al. 2020 | ThailandCollection date unreportedbasis not stated | sample value. | ||
| Anchovy · fish sauceDiviš et al. 2020 | ThailandCollection date unreportedbasis not stated | sample value. | ||
| Anchovy · fish sauceDiviš et al. 2020 | ThailandCollection date unreportedbasis not stated | sample value. | ||
| Anchovy · fish sauceDiviš et al. 2020 | ThailandCollection date unreportedbasis not stated | sample value. | ||
| Anchovy · fish sauceDiviš et al. 2020 | ThailandCollection date unreportedbasis not stated | sample value. | ||
| Anchovy · fish sauceDiviš et al. 2020 | ThailandCollection date unreportedbasis not stated | sample value. | ||
20 findings · 4 studies · 11 spread figures folded in | ||||
| Tuna · cannedCarter et al. 2025 | online retailers or stores in theCollection date unreportedbasis not stated | sample value. | ||
| Tuna · cannedCarter et al. 2025 | online retailers or stores in theCollection date unreportedbasis not stated | sample value. | ||
| Tuna · cannedCarter et al. 2025 | online retailers or stores in theCollection date unreportedbasis not stated | sample value. | ||
| Tuna · cannedCarter et al. 2025 | online retailers or stores in theCollection date unreportedbasis not stated | sample value. | ||
| Tuna · cannedFood 2019 | Retail/takeaway purchases across2013–2014 | mean. | ||
| Tuna · cannedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Tuna · cannedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 35–393 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 41–460 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 97–140 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 120–159 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 106–273 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 163–213 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 88–460 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 145–393 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 152–212 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 35–89 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 41–121 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
55 findings · 6 studies · 12 spread figures folded in | ||||
| Tuna · cookedWHO GEMS/Food | WHO region EURO2018 | median. | ||
| Tuna · cookedWHO GEMS/Food | WHO region PAHO2011–2016 | median. | ||
| Tuna · cookedWHO GEMS/Food | WHO region WPRO2014 | median. | ||
| Tuna · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 150–450 µg/kg (range) | ||
| Tuna · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Tuna · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Tuna · cookedVera et al. 2018 | AzoresCollection date unreported | mean. | ||
| Mackerel · cookedWHO GEMS/Food | WHO region PAHO2015–2016 | median. | ||
| Mackerel · cookedVera et al. 2018 | Atlantic OceanCollection date unreported | mean. | ||
| Herring · cookedWHO GEMS/Food | WHO region EURO2018 | median. | ||
| Herring · cookedWHO GEMS/Food | WHO region PAHO2015–2016 | median. | ||
| Sardine and pilchard · cookedWHO GEMS/Food | WHO region PAHO2015–2016 | median. | ||
| Salmon · cookedWHO GEMS/Food | WHO region EURO2018 | median. | ||
| Salmon · cookedWHO GEMS/Food | WHO region PAHO2015–2016 | median. | ||
| Salmon · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 26–30 µg/kg (range) | ||
| Salmon · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Salmon · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Trout and char · cookedWHO GEMS/Food | WHO region EURO2018 | median. | ||
| Trout and char · cookedGerman 2024 | Germany, Eastern region2012–2021basis not stated | mean. | ||
| Trout and char · cookedGerman 2024 | Germany, Northern region2012–2021basis not stated | mean. | ||
| Trout and char · cookedGerman 2024 | Germany, Southern region2012–2021basis not stated | mean. | ||
| Trout and char · cookedGerman 2024 | Germany, Western region2012–2021basis not stated | mean. | ||
| Cod · cookedWHO GEMS/Food | WHO region EURO2018 | median. | ||
| Cod · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Pollock and saithe · cookedWHO GEMS/Food | WHO region EURO2018 | median. | ||
| Pollock and saithe · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Hake · cookedVera et al. 2018 | South AfricaCollection date unreported | mean. | ||
| Hake · cookedVera et al. 2018 | South AmericaCollection date unreported | mean. | ||
| Plaice, flounder, sole and turbot · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 4.8–11 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Plaice, flounder, sole and turbot · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Plaice, flounder, sole and turbot · cookedVera et al. 2018 | ChannelCollection date unreported | mean. | ||
| Plaice, flounder, sole and turbot · cookedVera et al. 2018 | Goro, ItalyCollection date unreported | mean. | ||
| Halibut · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Sea bream and porgies · cookedVera et al. 2018 | Farmed, ItalyCollection date unreported | mean. | ||
| Grey mullet · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 16–24 µg/kg (range) | ||
| Grey mullet · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Grouper · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 100–240 µg/kg (range) | ||
| Grouper · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Croaker and drum · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 49–100 µg/kg (range) | ||
| Croaker and drum · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Pomfret · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 26–42 µg/kg (range) | ||
| Pomfret · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Scorpionfish and rockfish · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Anglerfish and monkfish · cookedVera et al. 2018 | Atlantic OceanCollection date unreported | mean. | ||
| Eel · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 87–160 µg/kg (range) | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 63–250 µg/kg (range) | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 33–79 µg/kg (range) | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 4–5 µg/kg (range) | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Carp and other cyprinids · cookedGerman 2024 | Germany, Eastern region2012–2021basis not stated | mean. | ||
| Carp and other cyprinids · cookedGerman 2024 | Germany, Northern region2012–2021basis not stated | mean. | ||
| Carp and other cyprinids · cookedGerman 2024 | Germany, Southern region2012–2021basis not stated | mean. | ||
| Carp and other cyprinids · cookedGerman 2024 | Germany, Western region2012–2021basis not stated | below LOD. | ||
| Catfish · cookedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | below LOD. | ||
| Other freshwater fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 80–140 µg/kg (range) | ||
| Other freshwater fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Freshwater fish, species not stated · cookedWHO GEMS/Food | WHO region PAHO2015 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region PAHO2015–2016 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region EURO2018 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region WPRO2008–2014 | median. | ||
| Fish, species not stated · cookedANSES 2026 | France retail2021–2022 | mean. | ||
| Fish, species not stated · cookedFood 2019 | Retail/takeaway purchases across2013–2014 | mean. | ||
435 findings · 26 studies · 92 spread figures folded in | ||||
| Tuna · fresh or rawWHO GEMS/Food | WHO region EURO2008–2017 | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region WPRO2008–2014 | median. | ||
| Tuna · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | mean.Same samples: 20–920 µg/kg (range) | ||
| Tuna · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | range. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | mean.Same samples: 260–1,080 µg/kg (range) | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | geometric mean. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | range. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | mean.Same samples: 380–800 µg/kg (range) | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | geometric mean. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | range. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | mean.Same samples: 260–1,080 µg/kg (range) | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | geometric mean. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | range. | ||
| Tuna · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 1,730 µg/kg (maximum) | ||
| Tuna · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Tuna · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Tuna · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Tuna · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Tuna · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Tuna · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Tuna · fresh or rawHsi et al. 2016 | Fish markets2007–2014 | mean. | ||
| Tuna · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Tuna · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Tuna · fresh or rawSimultaneous speciation… 2023 | Indian OceanCollection date unreported | mean. | ||
| Tuna · fresh or rawVera et al. 2018 | AzoresCollection date unreported | mean. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 180–570 µg/kg (range) | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 260–970 µg/kg (range) | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 250–690 µg/kg (range) | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 400–1,060 µg/kg (range) | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 40–230 µg/kg (range) | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 70–670 µg/kg (range) | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Tuna · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Bonito · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Swordfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 1,080 µg/kg (maximum) | ||
| Swordfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Swordfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Swordfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Swordfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Swordfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Swordfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Swordfish · fresh or rawHsi et al. 2016 | Fish markets2007–2014 | mean. | ||
| Swordfish · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Swordfish · fresh or rawMehouel et al. 2019 | coast of Algiers, Algeria2017 | mean.Same samples: 120–1,920 µg/kg (range) | ||
| Swordfish · fresh or rawMehouel et al. 2019 | coast of Algiers, Algeria2017 | range. | ||
| Swordfish · fresh or rawMehouel et al. 2019 | Algerian coasts2017 | mean.Same samples: 120–1,920 µg/kg (range) | ||
| Swordfish · fresh or rawMehouel et al. 2019 | Algerian coasts2017 | range. | ||
| Swordfish · fresh or rawMehouel et al. 2019 | coast of Bejaia, Algeria2017 | mean. | ||
| Swordfish · fresh or rawMehouel et al. 2019 | coast of Bejaia, Algeria2017 | range. | ||
| Swordfish · fresh or rawMehouel et al. 2019 | coast of Oran, Algeria2017 | mean.Same samples: 130–230 µg/kg (range) | ||
| Swordfish · fresh or rawMehouel et al. 2019 | coast of Oran, Algeria2017 | range. | ||
| Swordfish · fresh or rawSimultaneous speciation… 2023 | Pacific and Indian OceansCollection date unreported | mean. | ||
| Swordfish · fresh or rawSpecies-specific… 2025 | Reunion Islands, Indian Ocean2013–2022 | mean.Same samples: 160–810 µg/kg (range) | ||
| Swordfish · fresh or rawSpecies-specific… 2025 | Reunion Islands, Indian Ocean2013–2022 | range. | ||
| Swordfish · fresh or rawSpecies-specific… 2025 | Seychelles, Indian Ocean2013–2022 | mean.Same samples: 230–1,380 µg/kg (range) | ||
| Swordfish · fresh or rawSpecies-specific… 2025 | Seychelles, Indian Ocean2013–2022 | range. | ||
| Swordfish · fresh or rawSpecies-specific… 2025 | South Africa, Indian Ocean2013–2022 | mean.Same samples: 320–900 µg/kg (range) | ||
| Swordfish · fresh or rawSpecies-specific… 2025 | South Africa, Indian Ocean2013–2022 | range. | ||
| Swordfish · fresh or rawSpecies-specific… 2025 | New Caledonia, Pacific Ocean2013–2022 | sample value. | ||
| Swordfish · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 1,020–1,900 µg/kg (range) | ||
| Swordfish · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Swordfish · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | New Caledonia, Pacific Ocean2013–2022 | mean.Same samples: 440–1,030 µg/kg (range) | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | New Caledonia, Pacific Ocean2013–2022 | range. | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | Mauritius, Indian Ocean2013–2022 | mean.Same samples: 90–800 µg/kg (range) | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | Mauritius, Indian Ocean2013–2022 | range. | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | New Caledonia, Pacific Ocean2013–2022 | mean.Same samples: 70–940 µg/kg (range) | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | New Caledonia, Pacific Ocean2013–2022 | range. | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | New Caledonia, Pacific Ocean2013–2022 | mean.Same samples: 310–1,070 µg/kg (range) | ||
| Marlin and other billfish · fresh or rawSpecies-specific… 2025 | New Caledonia, Pacific Ocean2013–2022 | range. | ||
| Shark · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | mean.Same samples: 280–1,650 µg/kg (range) | ||
| Shark · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | range. | ||
| Shark · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Shark · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Shark · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Shark · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Shark · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Shark · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Shark · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Shark · fresh or rawDevelopment of… 2023 | Binuangeun fish auction2019 | mean.Same samples: 290–1,220 µg/kg (range) | ||
| Shark · fresh or rawDevelopment of… 2023 | Binuangeun fish auction2019 | range. | ||
| Shark · fresh or rawDevelopment of… 2023 | Binuangeun fish auction2019 | mean.Same samples: 220–630 µg/kg (range) | ||
| Shark · fresh or rawDevelopment of… 2023 | Binuangeun fish auction2019 | range. | ||
| Shark · fresh or rawDevelopment of… 2023 | Binuangeun fish auction2019 | mean.Same samples: 680–1,140 µg/kg (range) | ||
| Shark · fresh or rawDevelopment of… 2023 | Binuangeun fish auction2019 | range. | ||
| Shark · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 1,730 µg/kg (maximum) | ||
| Shark · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Shark · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Shark · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Shark · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Shark · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Shark · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Mediterranean Sea2017–2022basis not stated | min. | ||
| Shark · fresh or rawGlobal Patterns of… 2026 | Mediterranean Sea2017–2022basis not stated | max. | ||
| Shark · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 4.4–156 µg/kg (range) | ||
| Shark · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Shark · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Shark · fresh or rawSimultaneous speciation… 2023 | FranceCollection date unreported | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Ray and skate · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Ray and skate · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Ray and skate · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region EURO2008–2017 | median. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region WPRO2014 | median. | ||
| Mackerel · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 29–53 µg/kg (range) | ||
| Mackerel · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Mackerel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 1,110 µg/kg (maximum) | ||
| Mackerel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Mackerel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Mackerel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Mackerel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Mackerel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Mackerel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Mackerel · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 10.2–28.5 µg/kg (range) | ||
| Mackerel · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Mackerel · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Mackerel · fresh or rawHsi et al. 2016 | Fish markets2007–2014 | mean. | ||
| Mackerel · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Mackerel · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Mackerel · fresh or rawVera et al. 2018 | Atlantic OceanCollection date unreported | mean. | ||
| Mackerel · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 40–250 µg/kg (range) | ||
| Mackerel · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Mackerel · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| King and Spanish mackerel · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 2–20 µg/kg (range) | ||
| King and Spanish mackerel · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| King and Spanish mackerel · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 20–80 µg/kg (range) | ||
| King and Spanish mackerel · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| King and Spanish mackerel · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Horse mackerel, jacks and trevally · fresh or rawHsi et al. 2016 | Fish markets2007–2014 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreporteddry weight | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreported | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 90–310 µg/kg (range) | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 10–180 µg/kg (range) | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 60–190 µg/kg (range) | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 230–810 µg/kg (range) | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 30–130 µg/kg (range) | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Herring · fresh or rawWHO GEMS/Food | WHO region EURO2008–2018 | median. | ||
| Herring · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 63 µg/kg (maximum) | ||
| Herring · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Herring · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Herring · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Herring · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Herring · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Herring · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Herring · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 5.5–79.6 µg/kg (range) | ||
| Herring · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Herring · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region EURO2008–2017 | median. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region WPRO2014 | median. | ||
| Sardine and pilchard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 121 µg/kg (maximum) | ||
| Sardine and pilchard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sardine and pilchard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sardine and pilchard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sardine and pilchard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sardine and pilchard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sardine and pilchard · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Sardine and pilchard · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Sardine and pilchard · fresh or rawMehouel et al. 2019 | coast of Algiers, Algeria2017 | mean.Same samples: up to 40 µg/kg (range maximum) | ||
| Sardine and pilchard · fresh or rawMehouel et al. 2019 | coast of Algiers, Algeria2017 | range. | ||
| Sardine and pilchard · fresh or rawMehouel et al. 2019 | Algerian coasts2017 | mean.Same samples: up to 70 µg/kg (range maximum) | ||
| Sardine and pilchard · fresh or rawMehouel et al. 2019 | Algerian coasts2017 | range. | ||
| Sardine and pilchard · fresh or rawMehouel et al. 2019 | coast of Bejaia, Algeria2017 | mean.Same samples: 40–70 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawMehouel et al. 2019 | coast of Bejaia, Algeria2017 | range. | ||
| Sardine and pilchard · fresh or rawMehouel et al. 2019 | coast of Oran, Algeria2017 | not detected. | ||
| Sardine and pilchard · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 10–30 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Sardine and pilchard · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Sprat · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 18 µg/kg (maximum) | ||
| Sprat · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sprat · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sprat · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sprat · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sprat · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sprat · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Anchovy · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: up to 7 µg/kg (range maximum) | ||
| Anchovy · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Anchovy · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 112 µg/kg (maximum) | ||
| Anchovy · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Anchovy · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Anchovy · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Anchovy · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Anchovy · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Anchovy · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Anchovy · fresh or rawHsi et al. 2016 | Fish markets2007–2014 | mean. | ||
| Anchovy · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Shad, hilsa and other herrings · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 2–13 µg/kg (range) | ||
| Shad, hilsa and other herrings · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Shad, hilsa and other herrings · fresh or rawMethylmercury… 2021 | Lake Maggiore, Pallanza Basin2016–2017dry weight | mean. | ||
| Shad, hilsa and other herrings · fresh or rawMethylmercury… 2021 | Lake Maggiore, Pallanza Basin2016–2017dry weight | mean. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region WPRO2014 | median. | ||
| Salmon · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: up to 130 µg/kg (range maximum) | ||
| Salmon · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Salmon · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region EURO2008–2020 | median. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region WPRO2014 | median. | ||
| Trout and char · fresh or rawHsi et al. 2016 | Fish markets2007–2014 | mean. | ||
| Trout and char · fresh or rawSimultaneous speciation… 2023 | ANSES aquaculture facilitiesCollection date unreported | mean. | ||
| Trout and char · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: up to 20 µg/kg (range maximum) | ||
| Trout and char · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Trout and char · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region EURO2009–2017 | median. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region WPRO2014 | median. | ||
| Cod · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 10–52 µg/kg (range) | ||
| Cod · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Cod · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Cod · fresh or rawHsi et al. 2016 | Fish markets2007–2014 | mean. | ||
| Cod · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 20–170 µg/kg (range) | ||
| Cod · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Cod · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Haddock · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 7–48 µg/kg (range) | ||
| Haddock · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Haddock · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Pollock and saithe · fresh or rawCarter et al. 2025 | online retailers or stores in theCollection date unreportedbasis not stated | sample value. | ||
| Pollock and saithe · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 6–19 µg/kg (range); 6–28 µg/kg (range) | ||
| Pollock and saithe · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean. | ||
| Pollock and saithe · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Pollock and saithe · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Pollock and saithe · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 8.9–24.3 µg/kg (range) | ||
| Pollock and saithe · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Pollock and saithe · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Hake · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 200 µg/kg (maximum) | ||
| Hake · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Hake · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Hake · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Hake · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Hake · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Hake · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Hake · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 11–42.2 µg/kg (range) | ||
| Hake · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Hake · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Hake · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Hake · fresh or rawVera et al. 2018 | South AfricaCollection date unreported | mean. | ||
| Hake · fresh or rawVera et al. 2018 | South AmericaCollection date unreported | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 205 µg/kg (maximum) | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Plaice, flounder, sole and turbot · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 3.2–28 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 9.9–47.3 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawVera et al. 2018 | ChannelCollection date unreported | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawVera et al. 2018 | Goro, ItalyCollection date unreported | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 19–480 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Halibut · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 1,210 µg/kg (maximum) | ||
| Halibut · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Halibut · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Halibut · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Halibut · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Halibut · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Halibut · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 104 µg/kg (maximum) | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bass and barramundi · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Sea bass and barramundi · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 141 µg/kg (maximum) | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Sea bream and porgies · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Sea bream and porgies · fresh or rawLevels of Mercury,… 2021 | Mediterranean area2019 | sample value. | ||
| Sea bream and porgies · fresh or rawVera et al. 2018 | Farmed, ItalyCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 40–370 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Sea bream and porgies · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Grey mullet · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 144 µg/kg (maximum) | ||
| Grey mullet · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Grey mullet · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Grey mullet · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Grey mullet · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Grey mullet · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Grey mullet · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Croaker and drum · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 8–32 µg/kg (range) | ||
| Croaker and drum · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Hairtail and cutlassfish · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 3–236 µg/kg (range) | ||
| Hairtail and cutlassfish · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Hairtail and cutlassfish · fresh or rawHsi et al. 2016 | Fish markets2007–2014 | mean. | ||
| Barracuda · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreporteddry weight | mean. | ||
| Barracuda · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreported | mean. | ||
| Scorpionfish and rockfish · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 49–102 µg/kg (range) | ||
| Scorpionfish and rockfish · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Anglerfish and monkfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 370 µg/kg (maximum) | ||
| Anglerfish and monkfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Anglerfish and monkfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Anglerfish and monkfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Anglerfish and monkfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Anglerfish and monkfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Anglerfish and monkfish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Anglerfish and monkfish · fresh or rawVera et al. 2018 | Atlantic OceanCollection date unreported | mean. | ||
| Eel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 455 µg/kg (maximum) | ||
| Eel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Eel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Eel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Eel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Eel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Eel · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Other marine fish · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | mean.Same samples: 30–570 µg/kg (range) | ||
| Other marine fish · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | range. | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | mean.Same samples: 38–202 µg/kg (range) | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | median. | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | range. | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | mean.Same samples: 8.36–23.3 µg/kg (range) | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | median. | ||
| Other marine fish · fresh or rawDiet shifts drive… 2025 | central and eastern North Pacific2018–2023 | range. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 121 µg/kg (maximum) | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 73 µg/kg (maximum) | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Other marine fish · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Other marine fish · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | mean.Same samples: 34.4–122 µg/kg (range) | ||
| Other marine fish · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | median. | ||
| Other marine fish · fresh or rawHarding et al. 2018 | outer Bay of Fundy / approaches to2000–2003 | range. | ||
| Other marine fish · fresh or rawHsi et al. 2016 | Fish markets2007–2014 | mean. | ||
| Other marine fish · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | mean.Same samples: 40–80 µg/kg (range) | ||
| Other marine fish · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | median. | ||
| Other marine fish · fresh or rawWatanabe et al. 2017 | landed in various regions2014–2015basis not stated | range. | ||
| Tilapia · fresh or rawHsi et al. 2016 | Fish markets2007–2014 | mean. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 51 µg/kg (maximum) | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Carp and other cyprinids · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Carp and other cyprinids · fresh or rawMethylmercury… 2021 | Boesio River mouth2016–2017dry weight | mean. | ||
| Carp and other cyprinids · fresh or rawMethylmercury… 2021 | Boesio River mouth2016–2017dry weight | mean. | ||
| Carp and other cyprinids · fresh or rawMethylmercury… 2021 | Boesio River mouth2016–2017dry weight | mean. | ||
| Carp and other cyprinids · fresh or rawMethylmercury… 2021 | Boesio River mouth2016–2017dry weight | mean. | ||
| Catfish · fresh or rawCharacterized et al. 2025 | Leticia, ColombiaCollection date unreporteddry weight | sample value. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Catfish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Catfish · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreporteddry weight | mean. | ||
| Catfish · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreported | mean. | ||
| Perch, walleye and zander · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 77 µg/kg (maximum) | ||
| Perch, walleye and zander · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Perch, walleye and zander · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Perch, walleye and zander · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Perch, walleye and zander · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Perch, walleye and zander · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Perch, walleye and zander · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other cichlids · fresh or rawHealth Risk Assessment… 2023 | Atrato River, ColombiaCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Cienaga de Unguia & Tumarado zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Medio Atrato zone, Choco, Colombia2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Murindo & Vigia del Fuerte zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Rio Quito zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawDataset of concentration… 2020 | Riosucio & Carmen del Darien zone2019basis not stated | range. | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2023 | Atrato River, ColombiaCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2020 | median. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region WPRO2006–2021 | median. | ||
| Marine fish, species not stated · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | mean.Same samples: 20–1,240 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawA Study on Total… 2013 | distant-water fisheries2012basis not stated | range. | ||
| Marine fish, species not stated · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Marine fish, species not stated · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Marine fish, species not stated · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | range. | ||
| Marine fish, species not stated · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | range. | ||
| Marine fish, species not stated · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | range. | ||
| Marine fish, species not stated · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Marine fish, species not stated · fresh or rawDetermination of… 2022 | Mediterranean Sea2020 | mean. | ||
| Marine fish, species not stated · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: up to 236 µg/kg (range maximum) | ||
| Marine fish, species not stated · fresh or rawDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Marine fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 400 µg/kg (maximum) | ||
| Marine fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Marine fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Marine fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Marine fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Marine fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Marine fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Marine fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | mean.Same samples: up to 322 µg/kg (range maximum) | ||
| Marine fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | range. | ||
| Marine fish, species not stated · fresh or rawSuzuki et al. 2022 | not stated in primary2019–2020basis not stated | mean. | ||
| Marine fish, species not stated · fresh or rawSuzuki et al. 2022 | not stated in primary2019–2020basis not stated | mean. | ||
| Marine fish, species not stated · fresh or rawSuzuki et al. 2022 | not stated in primary2019–2020basis not stated | mean. | ||
| Marine fish, species not stated · fresh or rawSuzuki et al. 2022 | not stated in primary2019–2020basis not stated | mean. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2008–2019 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region WPRO2008 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 5,740 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 5,740 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 106 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Fish, species not stated · fresh or rawHsi et al. 2016 | Fish markets2007–2014 | mean. | ||
| Fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | mean.Same samples: up to 84 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | range. | ||
| Fish, species not stated · fresh or rawSuzuki et al. 2022 | not stated in primary2019–2020basis not stated | mean. | ||
14 findings · 2 studies · 1 spread figure folded in | ||||
| Tuna · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Shark · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Herring · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Herring · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Herring · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Herring · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Salmon · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Trout and char · smoked, dried, salted or fermentedGerman 2024 | Germany, Eastern region2012–2021basis not stated | mean. | ||
| Trout and char · smoked, dried, salted or fermentedGerman 2024 | Germany, Northern region2012–2021basis not stated | mean. | ||
| Trout and char · smoked, dried, salted or fermentedGerman 2024 | Germany, Southern region2012–2021basis not stated | mean. | ||
| Trout and char · smoked, dried, salted or fermentedGerman 2024 | Germany, Western region2012–2021basis not stated | mean. | ||
| Pollock and saithe · smoked, dried, salted or fermentedDistributed et al. 2022 | Agricultural and marine products2021 | mean.Same samples: 9–26 µg/kg (range) | ||
| Pollock and saithe · smoked, dried, salted or fermentedDistributed et al. 2022 | Agricultural and marine products2021 | range. | ||
| Halibut · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Eel · smoked, dried, salted or fermentedGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
23 findings · 7 studies · 4 spread figures folded in | ||||
| Herring · fish productGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Cod · fish productGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Carp and other cyprinids · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 30–37 µg/kg (range) | ||
| Carp and other cyprinids · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2014 | median. | ||
| Fish, species not stated · fish productANSES 2026 | France retail2021–2022 | mean. | ||
| Fish, species not stated · fish productANSES 2026 | France retail2021–2022 | mean. | ||
| Fish, species not stated · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 23–32 µg/kg (range) | ||
| Fish, species not stated · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 26 µg/kg (maximum) | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | mean.Same samples: 538 µg/kg (maximum) | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | mean. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | median. | ||
| Fish, species not stated · fish productEFSA 2012 | EU/EEA Member State official2002–2011 | max. | ||
| Fish, species not stated · fish productFood 2011 | Australian state/territory2008 | median. | ||
| Fish, species not stated · fish productFood 2019 | Retail/takeaway purchases across2013–2014 | mean. | ||
| Fish, species not stated · fish productGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | mean. | ||
| Fish, species not stated · fish productGerman 2024 | Germany, BfR MEAL Study2012–2021basis not stated | below LOD. | ||
8 findings · 2 studies · 1 spread figure folded in | ||||
| Tuna · cannedAnwar et al. 2021 | Aceh watersCollection date unreportedbasis not stated | mean.Same samples: 130–800 µg/kg (range) | ||
| Tuna · cannedAnwar et al. 2021 | Aceh watersCollection date unreportedbasis not stated | range. | ||
| Tuna · cannedAnwar et al. 2021 | Aceh watersCollection date unreportedbasis not stated | mean. | ||
| Tuna · cannedAnwar et al. 2021 | Aceh watersCollection date unreportedbasis not stated | mean. | ||
| Tuna · cannedAnwar et al. 2021 | Aceh watersCollection date unreportedbasis not stated | mean. | ||
| Tuna · cannedAnwar et al. 2021 | Aceh watersCollection date unreportedbasis not stated | mean. | ||
| Tuna · cannedBartels et al. 2023 | Cape Coast marketCollection date unreportedbasis not stated | mean. | ||
| Mackerel · cannedBartels et al. 2023 | Cape Coast marketCollection date unreportedbasis not stated | mean. | ||
| Sardine and pilchard · cannedBartels et al. 2023 | Cape Coast marketCollection date unreportedbasis not stated | mean. | ||
18 findings · 1 study | ||||
| Tuna · cookedWHO GEMS/Food | WHO region EURO2007–2008 | median. | ||
| Tuna · cookedWHO GEMS/Food | WHO region PAHO2007–2020 | median. | ||
| Tuna · cookedWHO GEMS/Food | WHO region WPRO2014 | median. | ||
| Mackerel · cookedWHO GEMS/Food | WHO region PAHO2009–2020 | median. | ||
| Herring · cookedWHO GEMS/Food | WHO region PAHO2013–2017 | median. | ||
| Sardine and pilchard · cookedWHO GEMS/Food | WHO region PAHO2009–2021 | median. | ||
| Salmon · cookedWHO GEMS/Food | WHO region EURO2007–2009 | median. | ||
| Salmon · cookedWHO GEMS/Food | WHO region PAHO2007–2017 | median. | ||
| Trout and char · cookedWHO GEMS/Food | WHO region PAHO2016–2017 | median. | ||
| Cod · cookedWHO GEMS/Food | WHO region PAHO2009–2017 | median. | ||
| Marine fish, species not stated · cookedWHO GEMS/Food | WHO region AFRO2018 | median. | ||
| Marine fish, species not stated · cookedWHO GEMS/Food | WHO region PAHO2007–2016 | median. | ||
| Freshwater fish, species not stated · cookedWHO GEMS/Food | WHO region AFRO2018 | median. | ||
| Freshwater fish, species not stated · cookedWHO GEMS/Food | WHO region PAHO2011–2019 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region PAHO2015–2016 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region AFRO2018 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region EURO2007–2009 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region WPRO1998–2014 | median. | ||
228 findings · 18 studies · 1 spread figure folded in | ||||
| Tuna · fresh or rawWHO GEMS/Food | WHO region AFRO2013–2020 | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region EURO1999–2002 | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region PAHO2016basis not stated | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region PAHO2007–2020 | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region WPRO1980–2014 | median. | ||
| Tuna · fresh or rawDigoarachchi et al. 2022 | Indian Ocean2015–2017basis not stated | range. | ||
| Tuna · fresh or rawDigoarachchi et al. 2022 | Indian Ocean station 12015–2017basis not stated | range. | ||
| Tuna · fresh or rawRalston et al. 2014 | not stated in this paperCollection date unreportedbasis not stated | mean. | ||
| Tuna · fresh or rawRalston et al. 2014 | not stated in this paperCollection date unreportedbasis not stated | mean. | ||
| Tuna · fresh or rawRalston et al. 2014 | not stated in this paperCollection date unreportedbasis not stated | mean. | ||
| Swordfish · fresh or rawWHO GEMS/Food | WHO region SEARO2017 | median. | ||
| Swordfish · fresh or rawDigoarachchi et al. 2022 | Indian Ocean, stations 1-42015–2017basis not stated | range. | ||
| Swordfish · fresh or rawRalston et al. 2014 | not stated in this paperCollection date unreportedbasis not stated | mean. | ||
| Marlin and other billfish · fresh or rawRalston et al. 2014 | not stated in this paperCollection date unreportedbasis not stated | mean.Same samples: up to 12,000 µg/kg (range maximum) | ||
| Marlin and other billfish · fresh or rawRalston et al. 2014 | not stated in this paperCollection date unreportedbasis not stated | range. | ||
| Shark · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Shark · fresh or rawRalston et al. 2014 | not stated in this paperCollection date unreportedbasis not stated | mean. | ||
| Shark · fresh or rawRalston et al. 2014 | not stated in this paperCollection date unreportedbasis not stated | mean. | ||
| Shark · fresh or rawSETAC EUROPE 35 TH… 2025 | fish markets on Buru Island andCollection date unreportedbasis not stated | max. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region EURO2000–2004 | median. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region PAHO2007–2020 | median. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region WPRO1978–2014 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreporteddry weight | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreported | mean. | ||
| Herring · fresh or rawWHO GEMS/Food | WHO region EURO2002–2005 | median. | ||
| Herring · fresh or rawWHO GEMS/Food | WHO region PAHO2007–2019 | median. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region EURO2000–2002 | median. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region PAHO2007–2019 | median. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region WPRO1981–2014 | median. | ||
| Sardine and pilchard · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region EURO2001–2005 | median. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region PAHO2016basis not stated | median. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region PAHO2007–2020 | median. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region WPRO1985–2014 | median. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region EURO2000–2005 | median. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region PAHO2007–2020 | median. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region WPRO1975–2014 | median. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region EURO2000–2014 | median. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region PAHO2007–2020 | median. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region WPRO2014 | median. | ||
| Haddock · fresh or rawWHO GEMS/Food | WHO region EURO2013–2015 | median. | ||
| Haddock · fresh or rawWHO GEMS/Food | WHO region PAHO2016–2017 | median. | ||
| Pollock and saithe · fresh or rawWHO GEMS/Food | WHO region EURO2014 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawWHO GEMS/Food | WHO region PAHO2016–2017 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Sea bream and porgies · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Grey mullet · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Snapper · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Grouper · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Grouper · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Croaker and drum · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Croaker and drum · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Emperors and grunts · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Emperors and grunts · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Barracuda · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Barracuda · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Barracuda · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreporteddry weight | mean. | ||
| Barracuda · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreported | mean. | ||
| Eel · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Other marine fish · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Tilapia · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | max. | ||
| Tilapia · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Bukuru unreclaimed mining pits2019basis not stated | mean. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Riyom control point2019basis not stated | sample value. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Bukuru unreclaimed mining pits2019basis not stated | not detected. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Riyom control point2019basis not stated | sample value. | ||
| Tilapia · fresh or rawShaalan 2024 | Damietta River Nile2022basis not stated | mean. | ||
| Tilapia · fresh or rawShaalan 2024 | El Rayah El Tawfeeky canal2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawComparison of Proximate… 2025 | Assistant Director FisheriesCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawComparison of Proximate… 2025 | Head Islam, near Vehari, PunjabCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawOF THE SAFETY OF FISH… 2023 | Private fish farmsCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawOF THE SAFETY OF FISH… 2023 | Private fish farmsCollection date unreportedbasis not stated | mean. | ||
| Catfish · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Catfish · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreporteddry weight | mean. | ||
| Catfish · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreported | mean. | ||
| Pike · fresh or rawLepak et al. 2023 | Crawford Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2023 | Elkhead Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2023 | Elkhead Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2023 | Harvey Gap Reservoir2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2023 | Lon Hagler Reservoir2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2023 | Martin Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2023 | McPhee Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2023 | Narraguinnep Reservoir2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2023 | Rifle Gap Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2023 | Sanchez Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2023 | Stagecoach Reservoir2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2023 | Totten Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2023 | Vallecito Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2023 | Wellington Reservoir2004–2013basis not stated | below LOD. | ||
| Pike · fresh or rawLepak et al. 2025 | Crawford reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2025 | Elkhead reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2025 | Harvey Gap reservoir2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2025 | Lon Hagler reservoir2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2025 | Martin reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2025 | McPhee reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2025 | Narraguinnep reservoir2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2025 | Rifle Gap reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2025 | Sanchez reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2025 | Stagecoach reservoir2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2025 | Totten reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2025 | Vallecito reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Pike · fresh or rawLepak et al. 2025 | Wellington reservoir2004–2013basis not stated | below LOD. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Barr Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Bonny Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Boyd Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Brush Hollow Reservoir2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Carter Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Chatfield Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Cherry Creek Reservoir2004–2013basis not stated | below LOD. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Douglass Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Horsetooth Reservoir2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Jackson Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Lon Hagler Reservoir2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Lonetree Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Loveland Reservoir, Colorado, USA2004–2013basis not stated | below LOD. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Martin Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | McPhee Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Narraguinnep Reservoir2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Nee Gronda Reservoir2004–2013basis not stated | below LOD. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | North Sterling Reservoir2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Pueblo Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Rifle Gap Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Sanchez Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Stagecoach Reservoir2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Totten Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Trinidad Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Union Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2023 | Vallecito Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Barr reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Bonny reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Boyd reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Brush Hollow reservoir2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Carter reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Chatfield reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Cherry Creek reservoir2004–2013basis not stated | below LOD. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Douglass reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Horsetooth reservoir2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Jackson reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Lon Hagler reservoir2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Lonetree reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Loveland reservoir, Colorado, USA2004–2013basis not stated | below LOD. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Martin reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | McPhee reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Narraguinnep reservoir2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Nee Gronda reservoir2004–2013basis not stated | below LOD. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | North Sterling reservoir2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Pueblo reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Rifle Gap reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Sanchez reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Stagecoach reservoir2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Totten reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Trinidad reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Union reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawLepak et al. 2025 | Vallecito reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2023 | Boulder City Reservoir2004–2013basis not stated | below LOD. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2023 | Boyd Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2023 | Chatfield Reservoir, Colorado, USA2004–2013basis not stated | below LOD. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2023 | Elkhead Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2023 | Horseshoe Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2023 | Lon Hagler Reservoir2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2023 | Loveland Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2023 | Martin Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2023 | McPhee Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2023 | Narraguinnep Reservoir2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2023 | Nee Gronda Reservoir2004–2013basis not stated | below LOD. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2023 | Pueblo Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2023 | Rifle Gap Reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2023 | Union Reservoir, Colorado, USA2004–2013basis not stated | below LOD. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2025 | Boulder City reservoir2004–2013basis not stated | below LOD. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2025 | Boyd reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2025 | Chatfield reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2025 | Elkhead reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2025 | Harvey Gap reservoir2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2025 | Horseshoe reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2025 | Lon Hagler reservoir2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2025 | Loveland reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2025 | Martin reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2025 | McPhee reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2025 | Narraguinnep reservoir2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2025 | Nee Gronda reservoir2004–2013basis not stated | below LOD. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2025 | Pueblo reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2025 | Rifle Gap reservoir, Colorado, USA2004–2013basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawLepak et al. 2025 | Union reservoir, Colorado, USA2004–2013basis not stated | below LOD. | ||
| Other freshwater fish · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region AFRO2015–2020 | median. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2016basis not stated | median. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2007–2020 | median. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region WPRO1972–2021 | median. | ||
| Marine fish, species not stated · fresh or rawBhoyroo et al. 2015 | EEZ of MauritiusCollection date unreported | range. | ||
| Marine fish, species not stated · fresh or rawBhoyroo et al. 2015 | EEZ of MauritiusCollection date unreported | range. | ||
| Marine fish, species not stated · fresh or rawBhoyroo et al. 2015 | EEZ of MauritiusCollection date unreported | range. | ||
| Marine fish, species not stated · fresh or rawHELCOM et al. 2017 | Åland Sea2011–2015 | range. | ||
| Marine fish, species not stated · fresh or rawHELCOM et al. 2017 | Bay of Mecklenburg, Baltic Sea2011–2015 | mean. | ||
| Marine fish, species not stated · fresh or rawHELCOM et al. 2017 | Bornholm Basin, Baltic Sea2011–2015 | mean. | ||
| Marine fish, species not stated · fresh or rawHELCOM et al. 2017 | Bothnian Sea2011–2015 | mean. | ||
| Marine fish, species not stated · fresh or rawHELCOM et al. 2017 | Eastern Gotland Basin, Baltic Sea2011–2015 | mean. | ||
| Marine fish, species not stated · fresh or rawHELCOM et al. 2017 | Kattegat, Baltic Sea2011–2015 | mean. | ||
| Marine fish, species not stated · fresh or rawHELCOM et al. 2017 | Kiel Bay, Baltic Sea2011–2015 | mean. | ||
| Marine fish, species not stated · fresh or rawHELCOM et al. 2017 | Northern Baltic Proper, Baltic Sea2011–2015 | mean. | ||
| Marine fish, species not stated · fresh or rawHELCOM et al. 2017 | Western Gotland Basin, Baltic Sea2011–2015 | mean. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2007–2020 | median. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | range. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | range. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2007–2020 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO1999–2020 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region WPRO1997–2008 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region SEARO2014–2016 | median. | ||
| Fish, species not stated · fresh or rawScientific Research… 2020 | caldera near Sea Diamond wreck2019basis not stated | below LOD. | ||
1 finding · 1 study | ||||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2014–2018 | median. | ||
2 findings · 1 study | ||||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region EURO2001–2002 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region WPRO2001–2002 | median. | ||
1 finding · 1 study | ||||
| Tuna · cannedFood 2019 | Retail/takeaway purchases across2013–2014 | not detected. | ||
5 findings · 3 studies | ||||
| Tuna · cookedWHO GEMS/Food | WHO region WPRO2014 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region EURO2017 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region WPRO2014 | median. | ||
| Fish, species not stated · cookedANSES 2026 | France retail2021–2022 | mean. | ||
| Fish, species not stated · cookedFood 2019 | Retail/takeaway purchases across2013–2014 | not detected. | ||
10 findings · 2 studies | ||||
| Tuna · fresh or rawWHO GEMS/Food | WHO region EURO2015–2018 | median. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region EURO2016–2017 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreporteddry weight | mean. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region EURO2016–2017 | median. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region EURO2018dry weight | median. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region EURO2015–2018 | median. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region EURO2017–2018 | median. | ||
| Barracuda · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreporteddry weight | mean. | ||
| Catfish · fresh or rawMERCURY SPECIATION IN… 2026 | Seafood Central Market of MexicoCollection date unreporteddry weight | mean. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2015–2019 | median. | ||
5 findings · 4 studies | ||||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2012–2017 | median. | ||
| Fish, species not stated · fish productANSES 2026 | France retail2021–2022 | mean. | ||
| Fish, species not stated · fish productANSES 2026 | France retail2021–2022 | mean. | ||
| Fish, species not stated · fish productFood 2011 | Australian state/territory2008 | median. | ||
| Fish, species not stated · fish productFood 2019 | Retail/takeaway purchases across2013–2014 | not detected. | ||
151 findings · 24 studies · 25 spread figures folded in | ||||
| Tuna · cannedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Tuna · cannedCantoral et al. 2024 | Mexico City retail outlets2022–2023basis not stated | mean.Same samples: 10–19 µg/kg (range) | ||
| Tuna · cannedCantoral et al. 2024 | Mexico City retail outlets2022–2023basis not stated | range. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDjedjibegovic et al. 2020 | Thailand2019 | mean.Same samples: 10–20 µg/kg (range) | ||
| Tuna · cannedDjedjibegovic et al. 2020 | Thailand2019 | range. | ||
| Tuna · cannedEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 5–64 µg/kg (range) | ||
| Tuna · cannedEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Tuna · cannedFood 2019 | Retail/takeaway purchases across2013–2014 | mean. | ||
| Tuna · cannedGladys et al. 2026 | Central Market of Lima2023 | range. | ||
| Tuna · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Tuna · cannedKosker et al. 2023 | local markets in Türkiye2021 | mean. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 18–51 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 13–35 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 15–213 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: up to 37 µg/kg (range maximum) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 17–22 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 14–29 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 12–14 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: up to 16 µg/kg (range maximum) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 12–18 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 17–21 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Tuna · cannedOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Tuna · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | not stated2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean.Same samples: 7–210 µg/kg (range) | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | range. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | max. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | below LOD. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | below LOD. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 0–4 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 2.6–7 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 0–7 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedUlusoy 2023 | label origin Holland; FAO area 672017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Iran2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Canada; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Seychelles2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Maldives2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Mauritius2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin The Ivory Coast2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Holland; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Spain2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Philippines2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Equator [Ecuador]2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin United Arab Emirates2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | developed countries2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | developing countries2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Algeria2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Argentina2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Brazil2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Equator [Ecuador]2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Morocco2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Portugal2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Indonesia2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Tunisia2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Spain; FAO area 512017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Indonesia2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Italy2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Turkey2017–2019 | mean. | ||
| Tuna · cannedVoegborlo et al. 1999 | caught by commercial vessels offCollection date unreported | mean.Same samples: 90–320 µg/kg (range) | ||
| Tuna · cannedVoegborlo et al. 1999 | caught by commercial vessels offCollection date unreported | range. | ||
| Mackerel · cannedDjedjibegovic et al. 2020 | Morocco2019 | mean.Same samples: 21–47 µg/kg (range) | ||
| Mackerel · cannedDjedjibegovic et al. 2020 | Morocco2019 | range. | ||
| Mackerel · cannedGu et al. 2014 | retail outlets2011 | not detected. | ||
| Mackerel · cannedNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: up to 20 µg/kg (range maximum) | ||
| Mackerel · cannedNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Mackerel · cannedNaess et al. 2020 | Norwegian retail market2015–2018 | mean. | ||
| Mackerel · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Herring · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedEvaluation of… 2025 | SupermarketCollection date unreportedbasis not stated | sample value. | ||
| Sardine and pilchard · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Sardine and pilchard · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Sardine and pilchard · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Sardine and pilchard · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Anchovy · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Anchovy · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Salmon · cannedBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Croaker and drum · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Hairtail and cutlassfish · cannedGu et al. 2014 | retail outlets2011 | not detected. | ||
| Carp and other cyprinids · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Fish, species not stated · cannedWHO GEMS/Food | WHO region EMRO2015–2016 | median. | ||
| Fish, species not stated · cannedWHO GEMS/Food | WHO region EURO2003–2006 | median. | ||
| Fish, species not stated · cannedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cannedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | mean.Same samples: 8.36–13.8 µg/kg (range) | ||
| Fish, species not stated · cannedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | median. | ||
| Fish, species not stated · cannedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | range. | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: up to 1,500 µg/kg (range maximum) | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: up to 8,560 µg/kg (range maximum) | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean. | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | below LOD. | ||
| Fish, species not stated · cannedFood 2016 | Major retailers, Dublin, Ireland2012–2014 | range. | ||
| Fish, species not stated · cannedKosker et al. 2023 | local markets in Türkiye2021 | mean.Same samples: 1–110 µg/kg (range) | ||
| Fish, species not stated · cannedKosker et al. 2023 | local markets in Türkiye2021 | range. | ||
| Fish, species not stated · cannedSalahel et al. 2025 | randomly selected local markets2022basis not stated | mean.Same samples: 8–11 µg/kg (range) | ||
| Fish, species not stated · cannedSalahel et al. 2025 | randomly selected local markets2022basis not stated | range. | ||
65 findings · 10 studies · 6 spread figures folded in | ||||
| Tuna · cookedWHO GEMS/Food | WHO region EURO2007–2015 | median. | ||
| Tuna · cookedWHO GEMS/Food | WHO region WPRO2010–2014 | median. | ||
| Tuna · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 13–30 µg/kg (range) | ||
| Tuna · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Mackerel · cookedWHO GEMS/Food | WHO region EURO2006–2017 | median. | ||
| Horse mackerel, jacks and trevally · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Herring · cookedWHO GEMS/Food | WHO region EURO2018 | median. | ||
| Sardine and pilchard · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Sardine and pilchard · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Sardine and pilchard · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Shad, hilsa and other herrings · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Shad, hilsa and other herrings · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Shad, hilsa and other herrings · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Salmon · cookedWHO GEMS/Food | WHO region EURO2007–2009 | median. | ||
| Salmon · cookedWHO GEMS/Food | WHO region PAHO2003–2017 | median. | ||
| Salmon · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Salmon · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Cod · cookedWHO GEMS/Food | WHO region PAHO2017 | median. | ||
| Cod · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Cod · cookedWang et al. 2020 | Jilin Province, China2015–2016basis not stated | mean. | ||
| Cod · cookedWang et al. 2020 | other areas of Jilin Province2015–2016basis not stated | mean. | ||
| Cod · cookedWang et al. 2020 | Songhua River Basin area2015–2016basis not stated | mean. | ||
| Pollock and saithe · cookedWHO GEMS/Food | WHO region PAHO2003–2017 | median. | ||
| Plaice, flounder, sole and turbot · cookedWHO GEMS/Food | WHO region WPRO2010–2011 | median. | ||
| Plaice, flounder, sole and turbot · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Sea bream and porgies · cookedAbbas 2023 | Private fish farm2022dry weight | mean. | ||
| Sea bream and porgies · cookedAbbas 2023 | Private fish farm2022dry weight | mean. | ||
| Sea bream and porgies · cookedAbbas 2023 | Private fish farm2022dry weight | mean. | ||
| Sea bream and porgies · cookedAbbas 2023 | Bardawil Lake, North Sinai, Egypt2022dry weight | mean. | ||
| Sea bream and porgies · cookedAbbas 2023 | Bardawil Lake, North Sinai, Egypt2022dry weight | mean. | ||
| Sea bream and porgies · cookedAbbas 2023 | Bardawil Lake, North Sinai, Egypt2022dry weight | mean. | ||
| Grey mullet · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Grouper · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Croaker and drum · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Pomfret · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 4 µg/kg (range maximum) | ||
| Pomfret · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 5–11 µg/kg (range) | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 7 µg/kg (range maximum) | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other marine fish · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Tilapia · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Carp and other cyprinids · cookedWHO GEMS/Food | WHO region WPRO2010–2011 | median. | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Carp and other cyprinids · cookedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · cookedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · cookedWang et al. 2020 | Jilin Province, China2015–2016basis not stated | mean. | ||
| Carp and other cyprinids · cookedWang et al. 2020 | other areas of Jilin Province2015–2016basis not stated | mean. | ||
| Carp and other cyprinids · cookedWang et al. 2020 | Songhua River Basin area2015–2016basis not stated | mean. | ||
| Other freshwater fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Bream (species group not stated) · cookedWHO GEMS/Food | WHO region WPRO2010 | median. | ||
| Marine fish, species not stated · cookedWHO GEMS/Food | WHO region AFRO2018 | median. | ||
| Marine fish, species not stated · cookedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | mean.Same samples: 1.98–57.1 µg/kg (range) | ||
| Marine fish, species not stated · cookedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | median. | ||
| Marine fish, species not stated · cookedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | range. | ||
| Freshwater fish, species not stated · cookedWHO GEMS/Food | WHO region AFRO2018 | median. | ||
| Freshwater fish, species not stated · cookedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | mean.Same samples: 0.59–4.31 µg/kg (range) | ||
| Freshwater fish, species not stated · cookedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | median. | ||
| Freshwater fish, species not stated · cookedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | range. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region AFRO2018 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region EURO2006–2019 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region PAHO2003–2017 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region WPRO1998–2014 | median. | ||
| Fish, species not stated · cookedANSES 2026 | France retail2021–2022 | mean. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Fish, species not stated · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Fish, species not stated · cookedWang et al. 2020 | Jilin Province, China2015–2016basis not stated | mean. | ||
675 findings · 89 studies · 122 spread figures folded in | ||||
| Tuna · fresh or rawWHO GEMS/Food | WHO region AFRO2018–2020 | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region EMRO2014–2019 | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region EURO1999–2019 | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region PAHO2003–2017 | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region WPRO2000–2008 | median. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | mean.Same samples: 4.52–41.9 µg/kg (range) | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | geometric mean. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | range. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | mean.Same samples: 2.43–23.2 µg/kg (range) | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | geometric mean. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | range. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | mean.Same samples: 2.43–41.9 µg/kg (range) | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | geometric mean. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | range. | ||
| Tuna · fresh or rawDigoarachchi et al. 2022 | Indian Ocean2015–2017basis not stated | not detected. | ||
| Tuna · fresh or rawDjedjibegovic et al. 2020 | Portugal2019 | mean. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 16–38 µg/kg (range) | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 11–26 µg/kg (range) | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–60 µg/kg (range) | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 10–60 µg/kg (range) | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Tuna · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Tuna · fresh or rawLehel et al. 2023 | Sri LankaCollection date unreported | mean.Same samples: 50–70 µg/kg (range) | ||
| Tuna · fresh or rawLehel et al. 2023 | Sri LankaCollection date unreported | range. | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 9–139 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 4–14 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 10–19 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 6–17 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawOktariani et al. 2023 | FAO Fishing Zone 572012–2016 | mean.Same samples: up to 74 µg/kg (range maximum) | ||
| Tuna · fresh or rawOktariani et al. 2023 | FAO Fishing Zone 572012–2016 | range. | ||
| Tuna · fresh or rawOktariani et al. 2023 | FAO Fishing Zone 712012–2016 | mean.Same samples: 6–387 µg/kg (range) | ||
| Tuna · fresh or rawOktariani et al. 2023 | FAO Fishing Zone 712012–2016 | range. | ||
| Tuna · fresh or rawOlmedo et al. 2013 | Canary Islands, Spain2009–2010 | median. | ||
| Tuna · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Tuna · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 1–2 µg/kg (range) | ||
| Tuna · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Tuna · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Swordfish · fresh or rawEFSA 2009 | EU Member States2003–2007basis not stated | mean.Same samples: 399 µg/kg (maximum) | ||
| Swordfish · fresh or rawEFSA 2009 | EU Member States2003–2007basis not stated | median. | ||
| Swordfish · fresh or rawEFSA 2009 | EU Member States2003–2007basis not stated | max. | ||
| Swordfish · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 1.3–19 µg/kg (range) | ||
| Swordfish · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Swordfish · fresh or rawOktariani et al. 2023 | FAO Fishing Zone 572012–2016 | range. | ||
| Swordfish · fresh or rawOktariani et al. 2023 | FAO Fishing Zone 712012–2016 | range. | ||
| Swordfish · fresh or rawOlmedo et al. 2013 | Galicia, Spain2009–2010 | median. | ||
| Swordfish · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 1–3 µg/kg (range) | ||
| Swordfish · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Marlin and other billfish · fresh or rawSmolikova et al. 2016 | Brno City markets, Czech Republic2015–2016 | mean. | ||
| Shark · fresh or rawWHO GEMS/Food | WHO region EURO2004–2007 | median. | ||
| Shark · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Shark · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Shark · fresh or rawOlmedo et al. 2013 | Basque Country, Spain2009–2010 | median. | ||
| Shark · fresh or rawOlmedo et al. 2013 | Valencia, Spain2009–2010 | median. | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 1–3 µg/kg (range) | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 1–2 µg/kg (range) | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | below LOD. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | below LOD. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | below LOD. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | below LOD. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | below LOD. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | below LOD. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | below LOD. | ||
| Ray and skate · fresh or rawSmolikova et al. 2016 | Brno City markets, Czech Republic2015–2016 | mean. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region EURO2000–2019 | median. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region PAHO2016 | median. | ||
| Mackerel · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Mackerel · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Mackerel · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 4–6 µg/kg (range) | ||
| Mackerel · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–20 µg/kg (range) | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–20 µg/kg (range) | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 10–30 µg/kg (range) | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Mackerel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Mackerel · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Mackerel · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Mackerel · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Mackerel · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Mackerel · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Mackerel · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| King and Spanish mackerel · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Horse mackerel, jacks and trevally · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawOlmedo et al. 2013 | Valencia, Spain2009–2010 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Herring · fresh or rawWHO GEMS/Food | WHO region EURO2000–2019 | median. | ||
| Herring · fresh or rawWHO GEMS/Food | WHO region PAHO2016 | median. | ||
| Herring · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 3–19 µg/kg (range) | ||
| Herring · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Herring · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean. | ||
| Herring · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | below LOD. | ||
| Herring · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Herring · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 44–55 µg/kg (range) | ||
| Herring · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Herring · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Herring · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 10–40 µg/kg (range) | ||
| Herring · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Herring · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region EMRO2015 | median. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region EURO2000–2019 | median. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region PAHO2016 | median. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region WPRO2000–2008 | median. | ||
| Sardine and pilchard · fresh or rawAkkaya et al. 2025 | Marmara region provinces, Türkiye2020–2022 | not detected. | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | SW Atlantic continental shelf2018 | below LOD. | ||
| Sardine and pilchard · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 10–171 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 3–51 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 4–84 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 10–110 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Sardine and pilchard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Sardine and pilchard · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Sardine and pilchard · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Sardine and pilchard · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Sardine and pilchard · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Anchovy · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Anchovy · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 150–330 µg/kg (range) | ||
| Anchovy · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Anchovy · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 75–572 µg/kg (range) | ||
| Anchovy · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Anchovy · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Anchovy · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 41–287 µg/kg (range) | ||
| Anchovy · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Anchovy · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Anchovy · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–380 µg/kg (range) | ||
| Anchovy · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Anchovy · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Anchovy · fresh or rawOlmedo et al. 2013 | Catalonia, Spain2009–2010 | median. | ||
| Anchovy · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Anchovy · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Anchovy · fresh or rawSimionov et al. 2023 | Fishing, Black Sea, BulgariaCollection date unreported | mean. | ||
| Shad, hilsa and other herrings · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Shad, hilsa and other herrings · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region EURO2001–2007 | median. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region WPRO1998–2005 | median. | ||
| Salmon · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 1–1 µg/kg (range) | ||
| Salmon · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Salmon · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 10–30 µg/kg (range) | ||
| Salmon · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–5 µg/kg (range) | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–20 µg/kg (range) | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 10–10 µg/kg (range) | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Salmon · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Salmon · fresh or rawOlmedo et al. 2013 | Norway2009–2010 | below LOD. | ||
| Salmon · fresh or rawPCBs and Heavy Metals… 2020 | caught at sea off Finnmark2017–2018 | below LOD. | ||
| Salmon · fresh or rawPCBs and Heavy Metals… 2020 | Lerøy Aurora farm2017–2018 | below LOD. | ||
| Salmon · fresh or rawPCBs and Heavy Metals… 2020 | Lopphavet, Finnmark, Norway2017–2018 | below LOD. | ||
| Salmon · fresh or rawSimionov et al. 2023 | Aquaculture, NorwayCollection date unreported | mean. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region EURO2018dry weight | median. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region EURO2000–2019 | median. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region PAHO2016 | median. | ||
| Trout and char · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean. | ||
| Trout and char · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | below LOD. | ||
| Trout and char · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Trout and char · fresh or rawLehel et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean.Same samples: 50–70 µg/kg (range) | ||
| Trout and char · fresh or rawLehel et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | range. | ||
| Trout and char · fresh or rawMajlesi et al. 2017 | Khersan River2016basis not stated | mean. | ||
| Trout and char · fresh or rawMajlesi et al. 2019 | Six raceway farms in three culture2018dry weight | mean. | ||
| Trout and char · fresh or rawMajlesi et al. 2019 | Site A2018dry weight | mean. | ||
| Trout and char · fresh or rawMajlesi et al. 2019 | Site B2018dry weight | mean. | ||
| Trout and char · fresh or rawMajlesi et al. 2019 | Site C2018dry weight | mean. | ||
| Trout and char · fresh or rawSimionov et al. 2023 | Aquaculture, RomaniaCollection date unreported | mean. | ||
| Whitefish and vendace · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 5–5 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Whitefish and vendace · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 3–24 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region EURO2000–2019 | median. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region PAHO2016 | median. | ||
| Cod · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 4–9 µg/kg (range) | ||
| Cod · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Cod · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–5 µg/kg (range) | ||
| Cod · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Cod · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Cod · fresh or rawOlmedo et al. 2013 | Atlantic Northeast2009–2010 | median. | ||
| Cod · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Haddock · fresh or rawWHO GEMS/Food | WHO region EURO2005 | median. | ||
| Haddock · fresh or rawWHO GEMS/Food | WHO region PAHO2016 | median. | ||
| Haddock · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: 4–4 µg/kg (range) | ||
| Haddock · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Haddock · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Haddock · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–5 µg/kg (range) | ||
| Haddock · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Haddock · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Haddock · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Pollock and saithe · fresh or rawWHO GEMS/Food | WHO region PAHO2016 | median. | ||
| Pollock and saithe · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: up to 14 µg/kg (range maximum) | ||
| Pollock and saithe · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L12019 | mean. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L22019 | not detected. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L32019 | mean. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L52019 | not detected. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L72019 | mean. | ||
| Whiting and blue whiting · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean. | ||
| Whiting and blue whiting · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | below LOD. | ||
| Whiting and blue whiting · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–40 µg/kg (range) | ||
| Whiting and blue whiting · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Whiting and blue whiting · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Whiting and blue whiting · fresh or rawOlmedo et al. 2013 | Galicia, Spain2009–2010 | below LOD. | ||
| Hake · fresh or rawDjedjibegovic et al. 2020 | Spain2019 | mean.Same samples: 2–4 µg/kg (range) | ||
| Hake · fresh or rawDjedjibegovic et al. 2020 | Spain2019 | range. | ||
| Hake · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean. | ||
| Hake · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | below LOD. | ||
| Hake · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Hake · fresh or rawOlmedo et al. 2013 | Valencia, Spain2009–2010 | below LOD. | ||
| Hake · fresh or rawOlmedo et al. 2013 | Mauritania2009–2010 | median. | ||
| Hake · fresh or rawOlmedo et al. 2013 | Mauritania2009–2010 | median. | ||
| Hake · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Hake · fresh or rawSimionov et al. 2023 | Spain; fishing area not specifiedCollection date unreported | mean. | ||
| Ling, tusk and other cod-like fish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean. | ||
| Ling, tusk and other cod-like fish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | below LOD. | ||
| Ling, tusk and other cod-like fish · fresh or rawReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Ling, tusk and other cod-like fish · fresh or rawRohonczy et al. 2024 | near Inukjuak2014–2017dry weight | mean. | ||
| Ling, tusk and other cod-like fish · fresh or rawRohonczy et al. 2024 | near Kuujjuaraapik2014–2017dry weight | mean. | ||
| Ling, tusk and other cod-like fish · fresh or rawRohonczy et al. 2024 | near Sanikiluaq2014–2017dry weight | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawWHO GEMS/Food | WHO region EURO2005 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawWHO GEMS/Food | WHO region EURO2003 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawWHO GEMS/Food | WHO region EURO2004–2005 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawWHO GEMS/Food | WHO region PAHO2016 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–40 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–20 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | below LOD. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | below LOD. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–5 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–5 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | mean.Same samples: 58–70 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawOlmedo et al. 2013 | Morocco2009–2010 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | below LOD. | ||
| Plaice, flounder, sole and turbot · fresh or rawTorabi et al. 2024 | Bushehr province ports2022 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawTorabi et al. 2024 | Bushehr province ports2022basis not stated | range. | ||
| Sea bass and barramundi · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 13–13 µg/kg (range) | ||
| Sea bass and barramundi · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Sea bass and barramundi · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Sea bass and barramundi · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Sea bass and barramundi · fresh or rawLevent 2022 | Sinop fish markets, Turkey2020 | mean. | ||
| Sea bass and barramundi · fresh or rawLevent 2022 | Sinop fish markets, Turkey2020 | mean. | ||
| Sea bass and barramundi · fresh or rawLevent 2022 | Sinop fish markets, Turkey2020 | mean. | ||
| Sea bass and barramundi · fresh or rawOlmedo et al. 2013 | Murcia, Spain2009–2010 | median. | ||
| Sea bass and barramundi · fresh or rawRay et al. 2025 | coastal and inland watersCollection date unreporteddry weight | mean. | ||
| Sea bass and barramundi · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | not detected. | ||
| Sea bream and porgies · fresh or rawAbbas 2023 | Private fish farm2022dry weight | mean. | ||
| Sea bream and porgies · fresh or rawAbbas 2023 | Bardawil Lake, North Sinai, Egypt2022dry weight | mean. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | below LOD. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 0.3–1 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | sample value. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 4.3–25 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 1.3–35 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: up to 18 µg/kg (range maximum) | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | coastal waters of TenerifeCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | Metropolitan zoneCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | North zoneCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | South zoneCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawOlmedo et al. 2013 | Murcia, Spain2009–2010 | median. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station I2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station II2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawSimionov et al. 2023 | Aquaculture, GreeceCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Sea bream and porgies · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Red mullet and goatfish · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Red mullet and goatfish · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 1–1 µg/kg (range) | ||
| Red mullet and goatfish · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Red mullet and goatfish · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | below LOD. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station I2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station II2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Grey mullet · fresh or rawAbbas et al. 2023 | El-Sharkia polyculture fishpondsCollection date unreporteddry weight | not detected. | ||
| Grey mullet · fresh or rawAbbas et al. 2023 | Kafr El-Sheikh polycultureCollection date unreporteddry weight | not detected. | ||
| Grey mullet · fresh or rawBakhshalizadeh et al. 2023 | Southern Caspian SeaCollection date unreportedbasis not stated | median.Same samples: 679 µg/kg (maximum) | ||
| Grey mullet · fresh or rawBakhshalizadeh et al. 2023 | Southern Caspian SeaCollection date unreportedbasis not stated | max. | ||
| Grey mullet · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Grey mullet · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Grey mullet · fresh or rawCirillo et al. 2010 | local fish markets2007 | median.Same samples: 12–14.1 µg/kg (range) | ||
| Grey mullet · fresh or rawCirillo et al. 2010 | local fish markets2007 | range. | ||
| Grey mullet · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 50–70 µg/kg (range) | ||
| Grey mullet · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Grey mullet · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Grey mullet · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Grey mullet · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Grey mullet · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Snapper · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Snapper · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Snapper · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Grouper · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Grouper · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Grouper · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Croaker and drum · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Croaker and drum · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Croaker and drum · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | mean.Same samples: 40–60 µg/kg (range) | ||
| Croaker and drum · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | range. | ||
| Croaker and drum · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Croaker and drum · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Emperors and grunts · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Emperors and grunts · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Emperors and grunts · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Emperors and grunts · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Pomfret · fresh or rawAlongkote et al. 2025 | not stated2025 | mean. | ||
| Pomfret · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Pomfret · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Pomfret · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | not detected. | ||
| Hairtail and cutlassfish · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | mean.Same samples: 0–60 µg/kg (range) | ||
| Hairtail and cutlassfish · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | range. | ||
| Hairtail and cutlassfish · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Barracuda · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Barracuda · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Barracuda · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Barracuda · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Barracuda · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Barracuda · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Barracuda · fresh or rawTorabi et al. 2024 | Bushehr province ports2022 | mean. | ||
| Barracuda · fresh or rawTorabi et al. 2024 | Bushehr province ports2022basis not stated | range. | ||
| Scorpionfish and rockfish · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Anglerfish and monkfish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean. | ||
| Anglerfish and monkfish · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | below LOD. | ||
| Anglerfish and monkfish · fresh or rawOlmedo et al. 2013 | Mauritania2009–2010 | median. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L12019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L32019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L42019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L52019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L62019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L82019 | mean. | ||
| Gurnard · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Gurnard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–20 µg/kg (range) | ||
| Gurnard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Gurnard · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Gurnard · fresh or rawSmolikova et al. 2016 | Brno City markets, Czech Republic2015–2016 | mean. | ||
| Eel · fresh or rawWHO GEMS/Food | WHO region EURO2005 | median. | ||
| Eel · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Eel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–170 µg/kg (range) | ||
| Eel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Eel · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Other marine fish · fresh or rawAlongkote et al. 2025 | not stated2025 | mean. | ||
| Other marine fish · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Other marine fish · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Other marine fish · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Other marine fish · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Other marine fish · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | mean.Same samples: 39–71 µg/kg (range) | ||
| Other marine fish · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | range. | ||
| Other marine fish · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Other marine fish · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: up to 10 µg/kg (range maximum) | ||
| Other marine fish · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Other marine fish · fresh or rawRay et al. 2025 | coastal and inland watersCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawRohonczy et al. 2024 | near Inukjuak2014–2017dry weight | mean. | ||
| Other marine fish · fresh or rawRohonczy et al. 2024 | near Kuujjuaraapik2014–2017dry weight | mean. | ||
| Other marine fish · fresh or rawRohonczy et al. 2024 | near Sanikiluaq2014–2017dry weight | mean. | ||
| Other marine fish · fresh or rawTorabi et al. 2024 | Bushehr province ports2022 | mean. | ||
| Other marine fish · fresh or rawTorabi et al. 2024 | Bushehr province ports2022basis not stated | range. | ||
| Other marine fish · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Tilapia · fresh or rawAbbas et al. 2023 | El-Sharkia polyculture fishpondsCollection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawAbbas et al. 2023 | Kafr El-Sheikh polycultureCollection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawBandara et al. 2010 | reservoirs near CRF patients'Collection date unreported | mean.Same samples: 0.5–90.7 µg/kg (range) | ||
| Tilapia · fresh or rawBandara et al. 2010 | reservoirs near CRF patients'Collection date unreported | range. | ||
| Tilapia · fresh or rawEgbe et al. 2023 | Lake Barombi KottoCollection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R1Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R2Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R3Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R4Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | max. | ||
| Tilapia · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | mean.Same samples: 4–5,500 µg/kg (range) | ||
| Tilapia · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | range. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Lake zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Bukuru unreclaimed mining pits2019basis not stated | mean. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Riyom control point2019basis not stated | sample value. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Bukuru unreclaimed mining pits2019basis not stated | mean. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Riyom control point2019basis not stated | sample value. | ||
| Tilapia · fresh or rawPáez-Osuna et al. 2024 | eleven dams, Sinaloa, NW Mexico2015–2016dry weight | range. | ||
| Tilapia · fresh or rawPáez-Osuna et al. 2024 | Dam 1: Luis Donaldo Colosio/Huites2015–2016dry weight | mean. | ||
| Tilapia · fresh or rawPáez-Osuna et al. 2024 | Dam 10: Aurelio Benassini V./El2015–2016dry weight | mean. | ||
| Tilapia · fresh or rawPáez-Osuna et al. 2024 | Dam 11: Picachos2015–2016dry weight | mean. | ||
| Tilapia · fresh or rawPáez-Osuna et al. 2024 | Dam 2: Miguel Hidalgo C./El Mahone2015–2016dry weight | mean. | ||
| Tilapia · fresh or rawPáez-Osuna et al. 2024 | Dam 3: Josefa Ortiz D./El Sabino2015–2016dry weight | mean. | ||
| Tilapia · fresh or rawPáez-Osuna et al. 2024 | Dam 4: Guillermo Blake/El Sabinal2015–2016dry weight | mean. | ||
| Tilapia · fresh or rawPáez-Osuna et al. 2024 | Dam 5: Gustavo Díaz O./Bacurato2015–2016dry weight | mean. | ||
| Tilapia · fresh or rawPáez-Osuna et al. 2024 | Dam 6: Eustaquio Buelna/Guamúchil2015–2016dry weight | mean. | ||
| Tilapia · fresh or rawPáez-Osuna et al. 2024 | Dam 7: Adolfo López M./El2015–2016dry weight | mean. | ||
| Tilapia · fresh or rawPáez-Osuna et al. 2024 | Dam 8: Sanalona2015–2016dry weight | mean. | ||
| Tilapia · fresh or rawPáez-Osuna et al. 2024 | Dam 9: José López P./El Comedero2015–2016dry weight | mean. | ||
| Tilapia · fresh or rawRay et al. 2025 | coastal and inland watersCollection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawShaalan 2024 | Damietta River Nile2022basis not stated | mean. | ||
| Tilapia · fresh or rawShaalan 2024 | El Rayah El Tawfeeky canal2022basis not stated | mean. | ||
| Tilapia · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | not detected. | ||
| Tilapia · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | not detected. | ||
| Carp and other cyprinids · fresh or rawWHO GEMS/Food | WHO region EURO2003–2007 | median. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Amarat reservoir2022basis not stated | mean.Same samples: 4–12 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Amarat reservoir2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Khawd reservoir2022basis not stated | mean.Same samples: 8–40 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Khawd reservoir2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Surur area2022basis not stated | mean.Same samples: 1–10 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Surur area2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawComparison of Proximate… 2025 | Assistant Director FisheriesCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawComparison of Proximate… 2025 | Head Islam, near Vehari, PunjabCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 12021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 22021–2022 | below LOD. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 32021–2022 | below LOD. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 42021–2022 | below LOD. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | mean.Same samples: 13 µg/kg (maximum) | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | max. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 1–6 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | below LOD. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | below LOD. | ||
| Carp and other cyprinids · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | mean.Same samples: 3–4 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | range. | ||
| Carp and other cyprinids · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | not detected. | ||
| Carp and other cyprinids · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | not detected. | ||
| Carp and other cyprinids · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | not detected. | ||
| Carp and other cyprinids · fresh or rawMajlesi et al. 2017 | Khersan River2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawOF THE SAFETY OF FISH… 2023 | Private fish farmsCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawOF THE SAFETY OF FISH… 2023 | Private fish farmsCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawRajeshkumar et al. 2018 | Meiliang Bay2016 | mean. | ||
| Carp and other cyprinids · fresh or rawRajeshkumar et al. 2018 | Meiliang Bay2016 | mean. | ||
| Carp and other cyprinids · fresh or rawRajeshkumar et al. 2018 | Meiliang Bay2016 | mean. | ||
| Carp and other cyprinids · fresh or rawRajeshkumar et al. 2018 | Meiliang Bay2016 | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Aquaculture, HungaryCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube Delta, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | not detected. | ||
| Carp and other cyprinids · fresh or rawSubhanullah et al. 2024 | Khall2021–2022Fish product as reported, mg/L | sample value. | ||
| Carp and other cyprinids · fresh or rawSubhanullah et al. 2024 | Thal Komrat2021–2022Fish product as reported, mg/L | sample value. | ||
| Carp and other cyprinids · fresh or rawSubhanullah et al. 2024 | Wari2021–2022basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreported | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreporteddry weight | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVičarová et al. 2016 | Domaninský reservoir2013–2014 | mean. | ||
| Carp and other cyprinids · fresh or rawVičarová et al. 2016 | Matějovský reservoir2013–2014 | mean. | ||
| Carp and other cyprinids · fresh or rawVičarová et al. 2016 | Pilská reservoir2013–2014 | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Faro, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Itaituba, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Porto TrombetasCollection date unreported | below LOD. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Catfish · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Catfish · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Catfish · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | mean.Same samples: 1–1,800 µg/kg (range) | ||
| Catfish · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | range. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawOlmedo et al. 2013 | Vietnam2009–2010 | median. | ||
| Catfish · fresh or rawSimionov et al. 2023 | Aquaculture, VietnamCollection date unreported | mean. | ||
| Catfish · fresh or rawSimionov et al. 2023 | Fishing, Danube Delta, RomaniaCollection date unreported | mean. | ||
| Catfish · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | not detected. | ||
| Catfish · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | not detected. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Badagry Creek2011–2013basis not stated | below LOD. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Badagry Creek2011–2013basis not stated | below LOD. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Lower zone, Badagry Creek, Nigeria2011–2013basis not stated | below LOD. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Middle zone2011–2013basis not stated | below LOD. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Upper zone, Badagry Creek, Nigeria2011–2013basis not stated | below LOD. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Badagry Creek2011–2013basis not stated | below LOD. | ||
| Pike · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 1–2 µg/kg (range) | ||
| Pike · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Pike · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | mean.Same samples: 3–5 µg/kg (range) | ||
| Pike · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | range. | ||
| Pike · fresh or rawMajlesi et al. 2017 | Khersan River2016basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawWHO GEMS/Food | WHO region EURO2003–2005 | median. | ||
| Perch, walleye and zander · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | mean. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 1–7 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: up to 2 µg/kg (range maximum) | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: up to 2 µg/kg (range maximum) | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Perch, walleye and zander · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | mean.Same samples: 3–4 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | range. | ||
| Perch, walleye and zander · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Black bass and sunfish · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | mean.Same samples: 1–3 µg/kg (range) | ||
| Black bass and sunfish · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | range. | ||
| Black bass and sunfish · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | mean.Same samples: 2–4 µg/kg (range) | ||
| Black bass and sunfish · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | range. | ||
| Black bass and sunfish · fresh or rawSimionov et al. 2023 | Aquaculture, ItalyCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Faro, western Pará, BrazilCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Itaituba, western Pará, BrazilCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Porto TrombetasCollection date unreported | below LOD. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | below LOD. | ||
| Snakehead · fresh or rawBandara et al. 2010 | reservoirs near CRF patients'Collection date unreported | mean.Same samples: 1.2–114 µg/kg (range) | ||
| Snakehead · fresh or rawBandara et al. 2010 | reservoirs near CRF patients'Collection date unreported | range. | ||
| Snakehead · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | mean.Same samples: 2–100 µg/kg (range) | ||
| Snakehead · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | range. | ||
| Snakehead · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Faro, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Itaituba, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: up to 1 µg/kg (range maximum) | ||
| Other freshwater fish · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Other freshwater fish · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Other freshwater fish · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawOlmedo et al. 2013 | Tanzania2009–2010 | median. | ||
| Other freshwater fish · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | not detected. | ||
| Bream (species group not stated) · fresh or rawWHO GEMS/Food | WHO region EURO2003–2005 | median. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region AFRO2018–2020 | median. | ||
| Marine fish, species not stated · fresh or rawAkkaya et al. 2025 | Marmara region provinces, Türkiye2020–2022 | range. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawBhoyroo et al. 2015 | EEZ of MauritiusCollection date unreported | not detected. | ||
| Marine fish, species not stated · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | range. | ||
| Marine fish, species not stated · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Marine fish, species not stated · fresh or rawBioaccumulation of… 2025 | Sea of Marmara, 8 stations2019 | range. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | mean.Same samples: up to 14.1 µg/kg (range maximum) | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | median. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | range. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | mean.Same samples: up to 17.7 µg/kg (range maximum) | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | median. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | range. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | mean.Same samples: up to 16.3 µg/kg (range maximum) | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | median. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | range. | ||
| Marine fish, species not stated · fresh or rawDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | mean.Same samples: 1.21–1.87 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | median. | ||
| Marine fish, species not stated · fresh or rawDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | range. | ||
| Marine fish, species not stated · fresh or rawDinesh et al. 2025 | Bay of BengalCollection date unreportedbasis not stated | mean. | ||
| Marine fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–5 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Marine fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | below LOD. | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | below LOD. | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | max. | ||
| Marine fish, species not stated · fresh or rawGladys et al. 2026 | Central Market of Lima2023 | mean.Same samples: 15–318 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawGladys et al. 2026 | Central Market of Lima2023 | range. | ||
| Marine fish, species not stated · fresh or rawJoint 2011 | Ghana2003–2009basis not stated | mean. | ||
| Marine fish, species not stated · fresh or rawJoint 2011 | Ghana2003–2009basis not stated | max. | ||
| Marine fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | mean.Same samples: up to 98 µg/kg (range maximum) | ||
| Marine fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | range. | ||
| Marine fish, species not stated · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Marine fish, species not stated · fresh or rawTorabi et al. 2024 | Bushehr province ports2022 | mean. | ||
| Marine fish, species not stated · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | not detected. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EMRO2014–2015 | median. | ||
| Freshwater fish, species not stated · fresh or rawDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | mean.Same samples: 0.54–7.72 µg/kg (range) | ||
| Freshwater fish, species not stated · fresh or rawDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | median. | ||
| Freshwater fish, species not stated · fresh or rawDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | range. | ||
| Freshwater fish, species not stated · fresh or rawFish (2026) | Lakes Burtnieks2024–2025basis not stated | below LOD. | ||
| Freshwater fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | below LOD. | ||
| Freshwater fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | below LOD. | ||
| Freshwater fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | max. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | range. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | range. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Freshwater fish, species not stated · fresh or rawRusko et al. 2026 | five Latvian inland lakes pooled2024–2025 | below LOD. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region AFRO2012dry weight | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EMRO2016–2019 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO1999–2019 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO1999–2018 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region SEARO2018–2020 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region WPRO1995–2008 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2003–2007 | median. | ||
| Fish, species not stated · fresh or rawChen et al. 2025 | Chongqing retail outlets2017–2021basis not stated | mean. | ||
| Fish, species not stated · fresh or rawChen et al. 2025 | Chongqing retail outlets2017–2021basis not stated | mean. | ||
| Fish, species not stated · fresh or rawChen et al. 2025 | Chongqing retail outlets2017–2021basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2009 | EU Member States2003–2007basis not stated | mean.Same samples: 280 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawEFSA 2009 | EU Member States2003–2007basis not stated | median. | ||
| Fish, species not stated · fresh or rawEFSA 2009 | EU Member States2003–2007basis not stated | max. | ||
| Fish, species not stated · fresh or rawEFSA 2009 | EU Member States2003–2007basis not stated | mean.Same samples: 660 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawEFSA 2009 | EU Member States2003–2007basis not stated | median. | ||
| Fish, species not stated · fresh or rawEFSA 2009 | EU Member States2003–2007basis not stated | max. | ||
| Fish, species not stated · fresh or rawEFSA 2009 | EU Member States2003–2007basis not stated | mean.Same samples: 300 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawEFSA 2009 | EU Member States2003–2007basis not stated | median. | ||
| Fish, species not stated · fresh or rawEFSA 2009 | EU Member States2003–2007basis not stated | max. | ||
| Fish, species not stated · fresh or rawEuropean 2012 | European Member States/EEA2003–2011basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEuropean 2012 | European Member States/EEA2003–2011basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Denmark national submission to1990–2002basis not stated | mean.Same samples: up to 17.2 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Denmark national submission to1990–2002basis not stated | median. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Denmark national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | France national submission to1990–2002basis not stated | mean.Same samples: up to 80 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | France national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Germany national submission to1990–2002basis not stated | mean.Same samples: up to 834 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Germany national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 1.3–900 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 0.5–6,230 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Italy national submission to SCOOP1990–2002basis not stated | mean.Same samples: up to 7.7 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Italy national submission to SCOOP1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Norway national submission to1990–2002basis not stated | mean.Same samples: up to 38 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Norway national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Portugal national submission to1990–2002basis not stated | mean.Same samples: up to 100 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Portugal national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Sweden national submission to1990–2002basis not stated | mean.Same samples: up to 110 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Sweden national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | mean.Same samples: 3.6–65.7 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | mean.Same samples: 10–60 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Belgium national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–810 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 10–140 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 19–144 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Belgium national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawFood 2016 | UK retail2013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawFood et al. 2014 | UK retail outlets, 2013-20142013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawFood et al. 2014 | UK retail outlets, 2013-20142013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawJoint 2011 | Australia2003–2009basis not stated | mean.Same samples: 15 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawJoint 2011 | Australia2003–2009basis not stated | max. | ||
| Fish, species not stated · fresh or rawJoint 2011 | France2003–2009basis not stated | mean.Same samples: 1,660 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawJoint 2011 | France2003–2009basis not stated | max. | ||
| Fish, species not stated · fresh or rawJoint 2011 | USA2003–2009basis not stated | mean.Same samples: 139 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawJoint 2011 | USA2003–2009basis not stated | max. | ||
| Fish, species not stated · fresh or rawJoint 2011 | USA2003–2009basis not stated | mean.Same samples: 29 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawJoint 2011 | USA2003–2009basis not stated | max. | ||
| Fish, species not stated · fresh or rawJoint 2011 | 6 countries/region2003–2009basis not stated | range. | ||
| Fish, species not stated · fresh or rawJoint 2011 | Singapore2003–2009basis not stated | not detected. | ||
| Fish, species not stated · fresh or rawJoint 2011 | 19 European countries2003–2009basis not stated | mean.Same samples: 660 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawJoint 2011 | 19 European countries2003–2009basis not stated | max. | ||
| Fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | mean.Same samples: up to 18 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | range. | ||
| Fish, species not stated · fresh or rawLim et al. 2015 | Supermarkets and marketplaces in2010–2011basis not stated | median. | ||
| Fish, species not stated · fresh or rawLoutfy et al. 2012 | 'All the samples were produced2007 | mean.Same samples: 50–170 µg/kg (range) | ||
| Fish, species not stated · fresh or rawLoutfy et al. 2012 | 'All the samples were produced2007 | range. | ||
| Fish, species not stated · fresh or rawOlmedo et al. 2013 | Granada, Spain2009–2010 | median. | ||
| Fish, species not stated · fresh or rawOlmedo et al. 2013 | Granada, Spain2009–2010 | median. | ||
| Fish, species not stated · fresh or rawOlmedo et al. 2013 | Granada, Spain2009–2010 | median. | ||
| Fish, species not stated · fresh or rawOlmedo et al. 2013 | Granada, Spain2009–2010 | median. | ||
| Fish, species not stated · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Fish, species not stated · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Fish, species not stated · fresh or rawScientific Research… 2020 | caldera near Sea Diamond wreck2019basis not stated | below LOD. | ||
| Fish, species not stated · fresh or rawSmolikova et al. 2016 | Brno City markets, Czech Republic2015–2016 | below LOD. | ||
| Fish, species not stated · fresh or rawSong et al. 2017 | supermarkets2011–2015basis not stated | mean. | ||
| Fish, species not stated · fresh or rawSong et al. 2017 | supermarkets2011–2015basis not stated | mean. | ||
34 findings · 6 studies · 8 spread figures folded in | ||||
| Herring · smoked, dried, salted or fermentedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 64–64 µg/kg (range) | ||
| Herring · smoked, dried, salted or fermentedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Herring · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | mean. | ||
| Grey mullet · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | mean. | ||
| Grey mullet · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | mean. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region AFRO2012dry weight | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region AFRO2013dry weight | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region EMRO2012–2015 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region EURO2003–2007 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region WPRO2001–2004 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region EMRO2015 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region EURO2003–2006 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets in Ouagadougou2020basis not stated | median.Same samples: up to 2,070 µg/kg (range maximum) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets in Ouagadougou2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Bobo Dioulasso2020basis not stated | median.Same samples: up to 120 µg/kg (range maximum) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Bobo Dioulasso2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Cinkasse2020basis not stated | median.Same samples: 80–2,070 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Cinkasse2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Dakola2020basis not stated | median.Same samples: up to 2,010 µg/kg (range maximum) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Dakola2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Niankologo2020basis not stated | median.Same samples: up to 540 µg/kg (range maximum) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Niankologo2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Ouagadougou2020basis not stated | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Ouagadougou2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBrima et al. 2025 | various African countries2023–2024dry weight | mean.Same samples: 50–400 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBrima et al. 2025 | various African countries2023–2024dry weight | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: up to 5,920 µg/kg (range maximum) | ||
| Fish, species not stated · smoked, dried, salted or fermentedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
4 findings · 2 studies | ||||
| Cod · fish oilWHO GEMS/Food | WHO region EURO2008–2015 | median. | ||
| Fish, species not stated · fish oilWHO GEMS/Food | WHO region EURO2003–2019 | median. | ||
| Fish, species not stated · fish oilEuropean 2012 | European Member States/EEA2003–2011basis not stated | mean. | ||
| Fish, species not stated · fish oilEuropean 2012 | European Member States/EEA2003–2011basis not stated | mean. | ||
61 findings · 12 studies · 19 spread figures folded in | ||||
| Cod · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean.Same samples: 1–6 µg/kg (range) | ||
| Cod · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | range. | ||
| Cod · fish productFechner et al. 2022 | German retail2017–2019basis not stated | mean. | ||
| Cod · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Cod · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Cod · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Cod · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Pollock and saithe · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 3–6 µg/kg (range) | ||
| Pollock and saithe · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Pollock and saithe · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | sample value. | ||
| Pollock and saithe · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | sample value. | ||
| Tilapia · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean.Same samples: 1–11 µg/kg (range) | ||
| Tilapia · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | range. | ||
| Carp and other cyprinids · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Catfish · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean.Same samples: 1–13 µg/kg (range) | ||
| Catfish · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 5–6 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 5–7 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 4–9 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: up to 4 µg/kg (range maximum) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: up to 21 µg/kg (range maximum) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 2–10 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 3–10 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 2–10 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EMRO2013–2017 | median. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2018basis not stated | median. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2003–2019 | median. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2013–2016 | median. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2003–2019 | median. | ||
| Fish, species not stated · fish productFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Fish, species not stated · fish productANSES 2026 | France retail2021–2022 | mean. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean. | ||
| Fish, species not stated · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | range. | ||
| Fish, species not stated · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 4 µg/kg (range maximum) | ||
| Fish, species not stated · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Fish, species not stated · fish productEFSA 2009 | EU Member States2003–2007basis not stated | mean.Same samples: 660 µg/kg (maximum) | ||
| Fish, species not stated · fish productEFSA 2009 | EU Member States2003–2007basis not stated | median. | ||
| Fish, species not stated · fish productEFSA 2009 | EU Member States2003–2007basis not stated | max. | ||
| Fish, species not stated · fish productEFSA 2009 | EU Member States2003–2007basis not stated | mean.Same samples: 1,300 µg/kg (maximum) | ||
| Fish, species not stated · fish productEFSA 2009 | EU Member States2003–2007basis not stated | median. | ||
| Fish, species not stated · fish productEFSA 2009 | EU Member States2003–2007basis not stated | max. | ||
| Fish, species not stated · fish productEuropean 2012 | European Member States/EEA2003–2011basis not stated | mean. | ||
| Fish, species not stated · fish productEuropean 2012 | European Member States/EEA2003–2011basis not stated | mean. | ||
| Fish, species not stated · fish productEuropean 2012 | European Member States/EEA2003–2011basis not stated | mean. | ||
| Fish, species not stated · fish productEuropean 2012 | European Member States/EEA2003–2011basis not stated | mean. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 16–36 µg/kg (range) | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–80 µg/kg (range) | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | mean.Same samples: 5–700 µg/kg (range) | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | median. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | the Netherlands national1990–2002basis not stated | range. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | mean.Same samples: 10–10 µg/kg (range) | ||
| Fish, species not stated · fish productEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | range. | ||
| Fish, species not stated · fish productKazimov et al. 2014 | Baku, AzerbaijanCollection date unreportedbasis not stated | max. | ||
| Fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
3 findings · 2 studies | ||||
| Fish, species not stated · fish sauceWHO GEMS/Food | WHO region EURO2004–2009 | median. | ||
| Fish, species not stated · fish sauceAbdullah 2009 | Fish sauce sample ACollection date unreportedbasis not stated | sample value. | ||
| Fish, species not stated · fish sauceAbdullah 2009 | Fish sauce sample BCollection date unreportedbasis not stated | sample value. | ||
156 findings · 26 studies · 32 spread figures folded in | ||||
| Tuna · cannedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Tuna · cannedAnwar et al. 2021 | Aceh watersCollection date unreportedbasis not stated | below LOD. | ||
| Tuna · cannedAnwar et al. 2021 | Aceh watersCollection date unreportedbasis not stated | below LOD. | ||
| Tuna · cannedAnwar et al. 2021 | Aceh watersCollection date unreportedbasis not stated | below LOD. | ||
| Tuna · cannedAnwar et al. 2021 | Aceh watersCollection date unreportedbasis not stated | below LOD. | ||
| Tuna · cannedBartels et al. 2023 | Cape Coast marketCollection date unreportedbasis not stated | mean. | ||
| Tuna · cannedCantoral et al. 2024 | Mexico City retail outlets2022–2023basis not stated | below LOD. | ||
| Tuna · cannedCantoral et al. 2024 | Mexico City retail outlets2022–2023basis not stated | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDjedjibegovic et al. 2020 | Thailand2019 | mean. | ||
| Tuna · cannedDjedjibegovic et al. 2020 | Thailand2019 | range. | ||
| Tuna · cannedEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 5–64 µg/kg (range) | ||
| Tuna · cannedEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Tuna · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 0.1–0.5 µg/kg (range) | ||
| Tuna · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Tuna · cannedGladys et al. 2026 | Central Market of Lima2023 | range. | ||
| Tuna · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Tuna · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Tuna · cannedKosker et al. 2023 | local markets in Türkiye2021 | mean. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: up to 33 µg/kg (range maximum) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: up to 64 µg/kg (range maximum) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: up to 49 µg/kg (range maximum) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: up to 45 µg/kg (range maximum) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: up to 47 µg/kg (range maximum) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: up to 51 µg/kg (range maximum) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 30–63 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 38–53 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: up to 42 µg/kg (range maximum) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | mean.Same samples: 32–47 µg/kg (range) | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | range. | ||
| Tuna · cannedOlmedo et al. 2013 | Spain2009–2010 | below LOD. | ||
| Tuna · cannedOlmedo et al. 2013 | Andalusia, Spain2009–2010 | below LOD. | ||
| Tuna · cannedOlmedo et al. 2013 | Spain2009–2010 | below LOD. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | not stated2009–2016 | below LOD. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean.Same samples: 26–920 µg/kg (range) | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | range. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedOrmaza-Gonzalez et al. 2020 | eastern Pacific2009–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | below LOD. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | below LOD. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | below LOD. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | below LOD. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | below LOD. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedPappalardo et al. 2017 | not stated2015–2016 | mean. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 70–110 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 90–130 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 90–130 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 80–320 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 110–130 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 90–120 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 80–100 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 80–140 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 70–320 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 40–252 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 50–270 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 0–100 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedUlusoy 2023 | label origin Holland; FAO area 672017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Iran2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Canada; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Seychelles2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Maldives2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Mauritius2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin The Ivory Coast2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Holland; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Spain2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Philippines2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Equator [Ecuador]2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin United Arab Emirates2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | developed countries2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | developing countries2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Algeria2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Argentina2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Brazil2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Equator [Ecuador]2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Morocco2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Portugal2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Indonesia2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Tunisia2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Spain; FAO area 512017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Indonesia2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Italy2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Turkey2017–2019 | mean. | ||
| Tuna · cannedVoegborlo et al. 1999 | caught by commercial vessels offCollection date unreported | mean.Same samples: 180–400 µg/kg (range) | ||
| Tuna · cannedVoegborlo et al. 1999 | caught by commercial vessels offCollection date unreported | range. | ||
| Mackerel · cannedBartels et al. 2023 | Cape Coast marketCollection date unreportedbasis not stated | mean. | ||
| Mackerel · cannedDjedjibegovic et al. 2020 | Morocco2019 | mean.Same samples: up to 10 µg/kg (range maximum) | ||
| Mackerel · cannedDjedjibegovic et al. 2020 | Morocco2019 | range. | ||
| Mackerel · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Mackerel · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Mackerel · cannedNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Mackerel · cannedNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Mackerel · cannedOlmedo et al. 2013 | Spain2009–2010 | below LOD. | ||
| Herring · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Sardine and pilchard · cannedBartels et al. 2023 | Cape Coast marketCollection date unreportedbasis not stated | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedEvaluation of… 2025 | SupermarketCollection date unreportedbasis not stated | sample value. | ||
| Sardine and pilchard · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Sardine and pilchard · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Sardine and pilchard · cannedOlmedo et al. 2013 | Spain2009–2010 | below LOD. | ||
| Sardine and pilchard · cannedOlmedo et al. 2013 | Spain2009–2010 | below LOD. | ||
| Anchovy · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Anchovy · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Salmon · cannedBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Salmon · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Croaker and drum · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Hairtail and cutlassfish · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Carp and other cyprinids · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Fish, species not stated · cannedWHO GEMS/Food | WHO region PAHO2011dry weight | median. | ||
| Fish, species not stated · cannedBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Fish, species not stated · cannedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | mean.Same samples: 8.6–72.8 µg/kg (range) | ||
| Fish, species not stated · cannedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | median. | ||
| Fish, species not stated · cannedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | range. | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 132–6,820 µg/kg (range) | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 250–620 µg/kg (range) | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · cannedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | sample value. | ||
| Fish, species not stated · cannedFood 2016 | Major retailers, Dublin, Ireland2012–2014 | range. | ||
| Fish, species not stated · cannedKosker et al. 2023 | local markets in Türkiye2021 | mean.Same samples: 100–430 µg/kg (range) | ||
| Fish, species not stated · cannedKosker et al. 2023 | local markets in Türkiye2021 | range. | ||
| Fish, species not stated · cannedSalahel et al. 2025 | randomly selected local markets2022basis not stated | mean.Same samples: 178–234 µg/kg (range) | ||
| Fish, species not stated · cannedSalahel et al. 2025 | randomly selected local markets2022basis not stated | range. | ||
73 findings · 10 studies · 14 spread figures folded in | ||||
| Tuna · cookedWHO GEMS/Food | WHO region EURO2007–2015 | median. | ||
| Tuna · cookedWHO GEMS/Food | WHO region SEARO2009–2016 | median. | ||
| Tuna · cookedWHO GEMS/Food | WHO region WPRO2010–2014 | median. | ||
| Tuna · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 4–5 µg/kg (range) | ||
| Tuna · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Mackerel · cookedWHO GEMS/Food | WHO region EURO2017 | median. | ||
| Mackerel · cookedWHO GEMS/Food | WHO region SEARO2008–2016 | median. | ||
| Horse mackerel, jacks and trevally · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Herring · cookedWHO GEMS/Food | WHO region EURO2018 | median. | ||
| Sardine and pilchard · cookedWHO GEMS/Food | WHO region SEARO2008–2016 | median. | ||
| Sardine and pilchard · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Sardine and pilchard · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Sardine and pilchard · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Shad, hilsa and other herrings · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Shad, hilsa and other herrings · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Shad, hilsa and other herrings · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Salmon · cookedWHO GEMS/Food | WHO region EURO2007–2009 | median. | ||
| Salmon · cookedWHO GEMS/Food | WHO region PAHO2000–2017 | median. | ||
| Salmon · cookedWHO GEMS/Food | WHO region SEARO2009–2016 | median. | ||
| Salmon · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Salmon · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 3–5 µg/kg (range) | ||
| Salmon · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Cod · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Cod · cookedWang et al. 2020 | Jilin Province, China2015–2016basis not stated | mean. | ||
| Cod · cookedWang et al. 2020 | other areas of Jilin Province2015–2016basis not stated | mean. | ||
| Cod · cookedWang et al. 2020 | Songhua River Basin area2015–2016basis not stated | mean. | ||
| Pollock and saithe · cookedWHO GEMS/Food | WHO region PAHO2000–2015 | median. | ||
| Plaice, flounder, sole and turbot · cookedWHO GEMS/Food | WHO region WPRO2010–2011 | median. | ||
| Plaice, flounder, sole and turbot · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 4–8 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Sea bream and porgies · cookedAbbas 2023 | Private fish farm2022dry weight | mean. | ||
| Sea bream and porgies · cookedAbbas 2023 | Private fish farm2022dry weight | mean. | ||
| Sea bream and porgies · cookedAbbas 2023 | Private fish farm2022dry weight | mean. | ||
| Sea bream and porgies · cookedAbbas 2023 | Bardawil Lake, North Sinai, Egypt2022dry weight | mean. | ||
| Sea bream and porgies · cookedAbbas 2023 | Bardawil Lake, North Sinai, Egypt2022dry weight | mean. | ||
| Sea bream and porgies · cookedAbbas 2023 | Bardawil Lake, North Sinai, Egypt2022dry weight | mean. | ||
| Grey mullet · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 11–26 µg/kg (range) | ||
| Grey mullet · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Grouper · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 5–7 µg/kg (range) | ||
| Grouper · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Croaker and drum · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 3–7 µg/kg (range) | ||
| Croaker and drum · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Pomfret · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 6–8 µg/kg (range) | ||
| Pomfret · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 7–18 µg/kg (range) | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 4–10 µg/kg (range) | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other marine fish · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Tilapia · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Carp and other cyprinids · cookedWHO GEMS/Food | WHO region WPRO2010–2011 | median. | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 4–10 µg/kg (range) | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 3–17 µg/kg (range) | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Carp and other cyprinids · cookedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · cookedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · cookedWang et al. 2020 | Jilin Province, China2015–2016basis not stated | mean. | ||
| Carp and other cyprinids · cookedWang et al. 2020 | other areas of Jilin Province2015–2016basis not stated | mean. | ||
| Carp and other cyprinids · cookedWang et al. 2020 | Songhua River Basin area2015–2016basis not stated | mean. | ||
| Other freshwater fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 8 µg/kg (range maximum) | ||
| Other freshwater fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Bream (species group not stated) · cookedWHO GEMS/Food | WHO region WPRO2010 | median. | ||
| Marine fish, species not stated · cookedWHO GEMS/Food | WHO region AFRO2018 | median. | ||
| Marine fish, species not stated · cookedWHO GEMS/Food | WHO region WPRO2009 | median. | ||
| Marine fish, species not stated · cookedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | mean.Same samples: up to 20.6 µg/kg (range maximum) | ||
| Marine fish, species not stated · cookedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | median. | ||
| Marine fish, species not stated · cookedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | range. | ||
| Freshwater fish, species not stated · cookedWHO GEMS/Food | WHO region AFRO2018 | median. | ||
| Freshwater fish, species not stated · cookedWHO GEMS/Food | WHO region PAHO2012–2015 | median. | ||
| Freshwater fish, species not stated · cookedWHO GEMS/Food | WHO region SEARO2009–2016 | median. | ||
| Freshwater fish, species not stated · cookedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | mean.Same samples: 2.2–36.1 µg/kg (range) | ||
| Freshwater fish, species not stated · cookedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | median. | ||
| Freshwater fish, species not stated · cookedDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | range. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region AFRO2018 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region EURO2007–2019 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region PAHO2003–2017 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region SEARO2013basis not stated | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region SEARO2009–2016 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region WPRO1998–2016 | median. | ||
| Fish, species not stated · cookedANSES 2026 | France retail2021–2022 | mean. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Fish, species not stated · cookedWang et al. 2020 | Jilin Province, China2015–2016basis not stated | mean. | ||
590 findings · 89 studies · 73 spread figures folded in | ||||
| Tuna · fresh or rawWHO GEMS/Food | WHO region AFRO2018–2020 | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region EURO1999–2019 | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region PAHO2000–2017 | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region SEARO2009–2016 | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region WPRO2000–2016 | median. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | mean.Same samples: 2.7–262 µg/kg (range) | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | geometric mean. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | range. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | mean.Same samples: 7.56–217 µg/kg (range) | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | geometric mean. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | range. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | mean.Same samples: 2.7–262 µg/kg (range) | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | geometric mean. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | range. | ||
| Tuna · fresh or rawDigoarachchi et al. 2022 | Indian Ocean2015–2017basis not stated | not detected. | ||
| Tuna · fresh or rawDjedjibegovic et al. 2020 | Portugal2019 | mean. | ||
| Tuna · fresh or rawDjedjibegovic et al. 2020 | Portugal2019 | range. | ||
| Tuna · fresh or rawLehel et al. 2023 | Sri LankaCollection date unreported | mean.Same samples: 300–1,590 µg/kg (range) | ||
| Tuna · fresh or rawLehel et al. 2023 | Sri LankaCollection date unreported | range. | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 62–683 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 5–18 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 3–7 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 5–17 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawOktariani et al. 2023 | FAO Fishing Zone 572012–2016 | range. | ||
| Tuna · fresh or rawOktariani et al. 2023 | FAO Fishing Zone 712012–2016 | range. | ||
| Tuna · fresh or rawOlmedo et al. 2013 | Canary Islands, Spain2009–2010 | below LOD. | ||
| Tuna · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Tuna · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 90–150 µg/kg (range) | ||
| Tuna · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Tuna · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Swordfish · fresh or rawOktariani et al. 2023 | FAO Fishing Zone 572012–2016 | range. | ||
| Swordfish · fresh or rawOktariani et al. 2023 | FAO Fishing Zone 712012–2016 | range. | ||
| Swordfish · fresh or rawOlmedo et al. 2013 | Galicia, Spain2009–2010 | below LOD. | ||
| Swordfish · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 80–160 µg/kg (range) | ||
| Swordfish · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Swordfish · fresh or rawSmolikova et al. 2016 | Brno City markets, Czech Republic2015–2016 | mean. | ||
| Shark · fresh or rawWHO GEMS/Food | WHO region SEARO2013–2015basis not stated | median. | ||
| Shark · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Shark · fresh or rawOlmedo et al. 2013 | Basque Country, Spain2009–2010 | below LOD. | ||
| Shark · fresh or rawOlmedo et al. 2013 | Valencia, Spain2009–2010 | below LOD. | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 100–320 µg/kg (range) | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 40–130 µg/kg (range) | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region EURO2000–2019 | median. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region PAHO2007–2017 | median. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region SEARO2008–2016 | median. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region WPRO2008–2015 | median. | ||
| Mackerel · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Mackerel · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Mackerel · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Mackerel · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | below LOD. | ||
| Mackerel · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Mackerel · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Mackerel · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Mackerel · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| King and Spanish mackerel · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Horse mackerel, jacks and trevally · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawOlmedo et al. 2013 | Valencia, Spain2009–2010 | below LOD. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Herring · fresh or rawWHO GEMS/Food | WHO region EURO2001–2019 | median. | ||
| Herring · fresh or rawWHO GEMS/Food | WHO region PAHO2008–2017 | median. | ||
| Herring · fresh or rawWHO GEMS/Food | WHO region WPRO2008–2009 | median. | ||
| Herring · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: up to 10 µg/kg (range maximum) | ||
| Herring · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region EURO1995–2019 | median. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region PAHO2017 | median. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region SEARO2011–2016 | median. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region WPRO2000–2009 | median. | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | SW Atlantic continental shelf2018 | below LOD. | ||
| Sardine and pilchard · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Sardine and pilchard · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | below LOD. | ||
| Sardine and pilchard · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Sardine and pilchard · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Sardine and pilchard · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Anchovy · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Anchovy · fresh or rawOlmedo et al. 2013 | Catalonia, Spain2009–2010 | below LOD. | ||
| Anchovy · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Anchovy · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Anchovy · fresh or rawSimionov et al. 2023 | Fishing, Black Sea, BulgariaCollection date unreported | mean. | ||
| Shad, hilsa and other herrings · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Shad, hilsa and other herrings · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region EURO2001 | median. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region PAHO2010–2017 | median. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region SEARO2009–2016 | median. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region WPRO1998–2008 | median. | ||
| Salmon · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | below LOD. | ||
| Salmon · fresh or rawOlmedo et al. 2013 | Norway2009–2010 | below LOD. | ||
| Salmon · fresh or rawPCBs and Heavy Metals… 2020 | caught at sea off Finnmark2017–2018 | below LOD. | ||
| Salmon · fresh or rawPCBs and Heavy Metals… 2020 | Lerøy Aurora farm2017–2018 | below LOD. | ||
| Salmon · fresh or rawPCBs and Heavy Metals… 2020 | Lopphavet, Finnmark, Norway2017–2018 | below LOD. | ||
| Salmon · fresh or rawSimionov et al. 2023 | Aquaculture, NorwayCollection date unreported | mean. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region EURO2018dry weight | median. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region EURO2000–2019 | median. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region PAHO2009–2017 | median. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region SEARO2011–2012 | median. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region WPRO2008–2009 | median. | ||
| Trout and char · fresh or rawLehel et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean.Same samples: 240–850 µg/kg (range) | ||
| Trout and char · fresh or rawLehel et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | range. | ||
| Trout and char · fresh or rawMajlesi et al. 2017 | Khersan River2016basis not stated | mean. | ||
| Trout and char · fresh or rawMajlesi et al. 2019 | Six raceway farms in three culture2018dry weight | mean. | ||
| Trout and char · fresh or rawMajlesi et al. 2019 | Site A2018dry weight | mean. | ||
| Trout and char · fresh or rawMajlesi et al. 2019 | Site B2018dry weight | mean. | ||
| Trout and char · fresh or rawSimionov et al. 2023 | Aquaculture, RomaniaCollection date unreported | mean. | ||
| Whitefish and vendace · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | below LOD. | ||
| Whitefish and vendace · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 10–30 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region EURO2000–2019 | median. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region PAHO2010–2017 | median. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region SEARO2010–2012 | median. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region WPRO2008 | median. | ||
| Cod · fresh or rawOlmedo et al. 2013 | Atlantic Northeast2009–2010 | below LOD. | ||
| Cod · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Haddock · fresh or rawWHO GEMS/Food | WHO region PAHO2017 | median. | ||
| Pollock and saithe · fresh or rawWHO GEMS/Food | WHO region PAHO2017 | median. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L12019 | not detected. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L22019 | mean. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L32019 | mean. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L52019 | mean. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L72019 | not detected. | ||
| Whiting and blue whiting · fresh or rawOlmedo et al. 2013 | Galicia, Spain2009–2010 | below LOD. | ||
| Hake · fresh or rawDjedjibegovic et al. 2020 | Spain2019 | mean. | ||
| Hake · fresh or rawDjedjibegovic et al. 2020 | Spain2019 | range. | ||
| Hake · fresh or rawOlmedo et al. 2013 | Valencia, Spain2009–2010 | median. | ||
| Hake · fresh or rawOlmedo et al. 2013 | Mauritania2009–2010 | below LOD. | ||
| Hake · fresh or rawOlmedo et al. 2013 | Mauritania2009–2010 | median. | ||
| Hake · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Hake · fresh or rawSimionov et al. 2023 | Spain; fishing area not specifiedCollection date unreported | mean. | ||
| Ling, tusk and other cod-like fish · fresh or rawReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawWHO GEMS/Food | WHO region PAHO2017 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawWHO GEMS/Food | WHO region SEARO2011–2012 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | mean.Same samples: 600–700 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawOlmedo et al. 2013 | Morocco2009–2010 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | below LOD. | ||
| Plaice, flounder, sole and turbot · fresh or rawTorabi et al. 2024 | Bushehr province ports2022 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawTorabi et al. 2024 | Bushehr province ports2022basis not stated | range. | ||
| Sea bass and barramundi · fresh or rawBalzani et al. 2026 | Dalyan Lake2021dry weight | mean. | ||
| Sea bass and barramundi · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Sea bass and barramundi · fresh or rawLevent 2022 | Sinop fish markets, Turkey2020 | mean. | ||
| Sea bass and barramundi · fresh or rawLevent 2022 | Sinop fish markets, Turkey2020 | mean. | ||
| Sea bass and barramundi · fresh or rawLevent 2022 | Sinop fish markets, Turkey2020 | mean. | ||
| Sea bass and barramundi · fresh or rawOlmedo et al. 2013 | Murcia, Spain2009–2010 | below LOD. | ||
| Sea bass and barramundi · fresh or rawRay et al. 2025 | coastal and inland watersCollection date unreporteddry weight | mean. | ||
| Sea bass and barramundi · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Sea bass and barramundi · fresh or rawSmolikova et al. 2016 | Brno City markets, Czech Republic2015–2016 | below LOD. | ||
| Sea bream and porgies · fresh or rawAbbas 2023 | Private fish farm2022dry weight | mean. | ||
| Sea bream and porgies · fresh or rawAbbas 2023 | Bardawil Lake, North Sinai, Egypt2022dry weight | mean. | ||
| Sea bream and porgies · fresh or rawBalzani et al. 2026 | Dalyan Lake2021dry weight | mean. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 520–630 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 3–10 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 48–265 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 10–40 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | coastal waters of TenerifeCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | Metropolitan zoneCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | North zoneCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | South zoneCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawOlmedo et al. 2013 | Murcia, Spain2009–2010 | below LOD. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station I2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station II2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawSimionov et al. 2023 | Aquaculture, GreeceCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Sea bream and porgies · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Red mullet and goatfish · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Red mullet and goatfish · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 30–30 µg/kg (range) | ||
| Red mullet and goatfish · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Red mullet and goatfish · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | below LOD. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station I2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station II2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Grey mullet · fresh or rawAbbas et al. 2023 | El-Sharkia polyculture fishpondsCollection date unreporteddry weight | mean. | ||
| Grey mullet · fresh or rawAbbas et al. 2023 | Kafr El-Sheikh polycultureCollection date unreporteddry weight | not detected. | ||
| Grey mullet · fresh or rawBakhshalizadeh et al. 2023 | Southern Caspian SeaCollection date unreportedbasis not stated | median.Same samples: 262 µg/kg (maximum) | ||
| Grey mullet · fresh or rawBakhshalizadeh et al. 2023 | Southern Caspian SeaCollection date unreportedbasis not stated | max. | ||
| Grey mullet · fresh or rawBalzani et al. 2026 | Dalyan Lake2021dry weight | mean. | ||
| Grey mullet · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Grey mullet · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Grey mullet · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 10–1,100 µg/kg (range) | ||
| Grey mullet · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Grey mullet · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Grey mullet · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Grey mullet · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Snapper · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Snapper · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Snapper · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Grouper · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Grouper · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Grouper · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Croaker and drum · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Croaker and drum · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Croaker and drum · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | mean.Same samples: 300–400 µg/kg (range) | ||
| Croaker and drum · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | range. | ||
| Croaker and drum · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Croaker and drum · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Emperors and grunts · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Emperors and grunts · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Emperors and grunts · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Emperors and grunts · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Pomfret · fresh or rawAlongkote et al. 2025 | not stated2025 | mean. | ||
| Pomfret · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Pomfret · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Pomfret · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Hairtail and cutlassfish · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | mean.Same samples: 300–1,000 µg/kg (range) | ||
| Hairtail and cutlassfish · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | range. | ||
| Hairtail and cutlassfish · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Barracuda · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Barracuda · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Barracuda · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Barracuda · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Barracuda · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Barracuda · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Barracuda · fresh or rawTorabi et al. 2024 | Bushehr province ports2022 | mean. | ||
| Barracuda · fresh or rawTorabi et al. 2024 | Bushehr province ports2022basis not stated | range. | ||
| Scorpionfish and rockfish · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Anglerfish and monkfish · fresh or rawOlmedo et al. 2013 | Mauritania2009–2010 | below LOD. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L12019 | not detected. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L32019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L42019 | not detected. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L52019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L62019 | not detected. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L82019 | not detected. | ||
| Gurnard · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Eel · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Other marine fish · fresh or rawAlongkote et al. 2025 | not stated2025 | mean. | ||
| Other marine fish · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Other marine fish · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Other marine fish · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Other marine fish · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Other marine fish · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | mean.Same samples: 100–700 µg/kg (range) | ||
| Other marine fish · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | range. | ||
| Other marine fish · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Other marine fish · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 6–14 µg/kg (range) | ||
| Other marine fish · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Other marine fish · fresh or rawRay et al. 2025 | coastal and inland watersCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawTorabi et al. 2024 | Bushehr province ports2022 | mean. | ||
| Other marine fish · fresh or rawTorabi et al. 2024 | Bushehr province ports2022basis not stated | range. | ||
| Other marine fish · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Tilapia · fresh or rawAbbas et al. 2023 | El-Sharkia polyculture fishpondsCollection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawAbbas et al. 2023 | Kafr El-Sheikh polycultureCollection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R1Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R2Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R3Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R4Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | max. | ||
| Tilapia · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | mean. | ||
| Tilapia · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | range. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Lake zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Bukuru unreclaimed mining pits2019basis not stated | mean. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Riyom control point2019basis not stated | sample value. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Bukuru unreclaimed mining pits2019basis not stated | mean. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Riyom control point2019basis not stated | not detected. | ||
| Tilapia · fresh or rawRay et al. 2025 | coastal and inland watersCollection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawSawe et al. 2023 | Lake Manyara, Tanzania2022dry weight | mean. | ||
| Tilapia · fresh or rawShaalan 2024 | Damietta River Nile2022basis not stated | mean. | ||
| Tilapia · fresh or rawShaalan 2024 | El Rayah El Tawfeeky canal2022basis not stated | mean. | ||
| Tilapia · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Tilapia · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Amarat reservoir2022basis not stated | mean.Same samples: 10–40 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Amarat reservoir2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Khawd reservoir2022basis not stated | mean.Same samples: 30–90 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Khawd reservoir2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Surur area2022basis not stated | mean.Same samples: 10–30 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Surur area2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawComparison of Proximate… 2025 | Assistant Director FisheriesCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawComparison of Proximate… 2025 | Assistant Director FisheriesCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawComparison of Proximate… 2025 | Head Islam, near Vehari, PunjabCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawComparison of Proximate… 2025 | Head Islam, near Vehari, PunjabCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 12021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 22021–2022 | below LOD. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 32021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 42021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva sites 1-42021–2022 | range. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | below LOD. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | below LOD. | ||
| Carp and other cyprinids · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | below LOD. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | mean.Same samples: 49–106 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | range. | ||
| Carp and other cyprinids · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawMajlesi et al. 2017 | Khersan River2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawOF THE SAFETY OF FISH… 2023 | Private fish farmsCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawOF THE SAFETY OF FISH… 2023 | Private fish farmsCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawRajeshkumar et al. 2018 | Meiliang Bay2016 | mean. | ||
| Carp and other cyprinids · fresh or rawRajeshkumar et al. 2018 | Meiliang Bay2016 | mean. | ||
| Carp and other cyprinids · fresh or rawRajeshkumar et al. 2018 | Meiliang Bay2016 | mean. | ||
| Carp and other cyprinids · fresh or rawRajeshkumar et al. 2018 | Meiliang Bay2016 | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Aquaculture, HungaryCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube Delta, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Carp and other cyprinids · fresh or rawSubhanullah et al. 2024 | Panjkora River, Dir, Pakistan2021–2022basis not stated | max. | ||
| Carp and other cyprinids · fresh or rawSubhanullah et al. 2024 | Khall2021–2022Fish product as reported, mg/L | sample value. | ||
| Carp and other cyprinids · fresh or rawSubhanullah et al. 2024 | Sheringal2021–2022Fish product as reported, mg/L | sample value. | ||
| Carp and other cyprinids · fresh or rawSubhanullah et al. 2024 | Thal Komrat2021–2022Fish product as reported, mg/L | sample value. | ||
| Carp and other cyprinids · fresh or rawSubhanullah et al. 2024 | Timergara2021–2022Fish product as reported, mg/L | sample value. | ||
| Carp and other cyprinids · fresh or rawSubhanullah et al. 2024 | Wari2021–2022basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreported | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreporteddry weight | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake VictoriaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · fresh or rawVičarová et al. 2016 | Domaninský reservoir2013–2014 | mean. | ||
| Carp and other cyprinids · fresh or rawVičarová et al. 2016 | Matějovský reservoir2013–2014 | mean. | ||
| Carp and other cyprinids · fresh or rawVičarová et al. 2016 | Pilská reservoir2013–2014 | mean. | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | mean.Same samples: 170–760 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | range. | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | mean.Same samples: 130–650 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | range. | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | mean.Same samples: 300–990 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | range. | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | mean.Same samples: 600–980 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | range. | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | mean.Same samples: 100–850 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawZolfaghari 2018 | Hamun wetlandsCollection date unreporteddry weight | range. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Faro, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Itaituba, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Porto TrombetasCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Catfish · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Catfish · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Catfish · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | mean.Same samples: 70–4,000 µg/kg (range) | ||
| Catfish · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | range. | ||
| Catfish · fresh or rawMariadi et al. 2017 | traditional marketCollection date unreportedbasis not stated | sample value. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawOlmedo et al. 2013 | Vietnam2009–2010 | below LOD. | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara, Tanzania2022dry weight | mean. | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | mean.Same samples: 430–640 µg/kg (range) | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | range. | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | mean.Same samples: 720–810 µg/kg (range) | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | range. | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | mean.Same samples: 410–720 µg/kg (range) | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | range. | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | mean.Same samples: 380–570 µg/kg (range) | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | range. | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | mean.Same samples: 530–670 µg/kg (range) | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | range. | ||
| Catfish · fresh or rawSimionov et al. 2023 | Aquaculture, VietnamCollection date unreported | mean. | ||
| Catfish · fresh or rawSimionov et al. 2023 | Fishing, Danube Delta, RomaniaCollection date unreported | mean. | ||
| Catfish · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Catfish · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Badagry Creek2011–2013basis not stated | range. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Badagry Creek2011–2013basis not stated | mean. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Badagry Creek2011–2013basis not stated | mean. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Lower zone, Badagry Creek, Nigeria2011–2013basis not stated | mean. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Middle zone2011–2013basis not stated | mean. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Upper zone, Badagry Creek, Nigeria2011–2013basis not stated | mean. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Badagry Creek2011–2013basis not stated | mean. | ||
| Pike · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: up to 20 µg/kg (range maximum) | ||
| Pike · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Pike · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | mean.Same samples: 34–74 µg/kg (range) | ||
| Pike · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | range. | ||
| Pike · fresh or rawMajlesi et al. 2017 | Khersan River2016basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | mean. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: up to 20 µg/kg (range maximum) | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 10–204 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | below LOD. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Perch, walleye and zander · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | mean.Same samples: 45–87 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | range. | ||
| Perch, walleye and zander · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | Valdeazogues River transectCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | Castilseras reservoirCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | El Entredicho open pit lakeCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | La Colada reservoirCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PLPCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PPACollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PPMCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PTHCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | mean.Same samples: 51–115 µg/kg (range) | ||
| Black bass and sunfish · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | range. | ||
| Black bass and sunfish · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | mean.Same samples: 17–43 µg/kg (range) | ||
| Black bass and sunfish · fresh or rawMahjoub et al. 2021 | Mechraa-Hammadi Dam2017–2018 | range. | ||
| Black bass and sunfish · fresh or rawSimionov et al. 2023 | Aquaculture, ItalyCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Faro, western Pará, BrazilCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Itaituba, western Pará, BrazilCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Porto TrombetasCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | mean. | ||
| Snakehead · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | mean.Same samples: 160–340 µg/kg (range) | ||
| Snakehead · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | range. | ||
| Snakehead · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Faro, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Itaituba, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | below LOD. | ||
| Other freshwater fish · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Other freshwater fish · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawOlmedo et al. 2013 | Tanzania2009–2010 | below LOD. | ||
| Other freshwater fish · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region AFRO2018–2020 | median. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2010dry weight | median. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2007–2018 | median. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region WPRO2007–2016 | median. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawBhoyroo et al. 2015 | EEZ of MauritiusCollection date unreported | range. | ||
| Marine fish, species not stated · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | mean.Same samples: up to 151 µg/kg (range maximum) | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | median. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | range. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | mean.Same samples: up to 541 µg/kg (range maximum) | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | median. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | range. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | mean.Same samples: up to 438 µg/kg (range maximum) | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | median. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | range. | ||
| Marine fish, species not stated · fresh or rawDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | mean.Same samples: up to 14.8 µg/kg (range maximum) | ||
| Marine fish, species not stated · fresh or rawDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | median. | ||
| Marine fish, species not stated · fresh or rawDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | range. | ||
| Marine fish, species not stated · fresh or rawDinesh et al. 2025 | Bay of BengalCollection date unreportedbasis not stated | mean. | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | below LOD. | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | below LOD. | ||
| Marine fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | max. | ||
| Marine fish, species not stated · fresh or rawGladys et al. 2026 | Central Market of Lima2023 | mean.Same samples: 3–16 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawGladys et al. 2026 | Central Market of Lima2023 | range. | ||
| Marine fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | mean.Same samples: 2–47 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | range. | ||
| Marine fish, species not stated · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Marine fish, species not stated · fresh or rawTorabi et al. 2024 | Bushehr province ports2022 | mean. | ||
| Marine fish, species not stated · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2010dry weight | median. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2007–2017 | median. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region SEARO2008–2016basis not stated | median. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region SEARO2009–2016 | median. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region WPRO2007–2009 | median. | ||
| Freshwater fish, species not stated · fresh or rawDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | mean.Same samples: 5.2–23.6 µg/kg (range) | ||
| Freshwater fish, species not stated · fresh or rawDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | median. | ||
| Freshwater fish, species not stated · fresh or rawDabeka et al. 1995 | Retail, Canada1985–1988basis not stated | range. | ||
| Freshwater fish, species not stated · fresh or rawFish (2026) | Lakes Burtnieks2024–2025basis not stated | below LOD. | ||
| Freshwater fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | below LOD. | ||
| Freshwater fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | below LOD. | ||
| Freshwater fish, species not stated · fresh or rawGarofalo et al. 2025 | worldwide2014–2023 | max. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean.Same samples: 92–659 µg/kg (range) | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | range. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Freshwater fish, species not stated · fresh or rawInternational Journal… 2021 | Nyeri County, KenyaCollection date unreporteddry weight | mean. | ||
| Freshwater fish, species not stated · fresh or rawRusko et al. 2026 | five Latvian inland lakes pooled2024–2025 | below LOD. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region WPRO2007–2008 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region AFRO2012dry weight | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO1995–2019 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2011–2017 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region SEARO2008–2016basis not stated | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region SEARO2009–2016 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region WPRO1998–2016 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2009–2017 | median. | ||
| Fish, species not stated · fresh or rawChen et al. 2025 | Chongqing retail outlets2017–2021basis not stated | mean. | ||
| Fish, species not stated · fresh or rawChen et al. 2025 | Chongqing retail outlets2017–2021basis not stated | mean. | ||
| Fish, species not stated · fresh or rawChen et al. 2025 | Chongqing retail outlets2017–2021basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2010 | EU Member States and Norway2003–2008basis not stated | mean.Same samples: 2,000 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawEFSA 2010 | EU Member States and Norway2003–2008basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2010 | EU Member States and Norway2003–2008basis not stated | median. | ||
| Fish, species not stated · fresh or rawEFSA 2010 | EU Member States and Norway2003–2008basis not stated | below LOD. | ||
| Fish, species not stated · fresh or rawEFSA 2010 | EU Member States and Norway2003–2008basis not stated | max. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Belgium national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Denmark national submission to1990–2002basis not stated | below LOD. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Denmark national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | France national submission to1990–2002basis not stated | mean.Same samples: up to 600 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | France national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Germany national submission to1990–2002basis not stated | mean.Same samples: up to 570 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Germany national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 10–413 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | mean.Same samples: up to 130 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Italy national submission to SCOOP1990–2002basis not stated | mean.Same samples: 25–150 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Italy national submission to SCOOP1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Norway national submission to1990–2002basis not stated | mean.Same samples: 10–50 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Norway national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Portugal national submission to1990–2002basis not stated | mean.Same samples: up to 300 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Portugal national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Sweden national submission to1990–2002basis not stated | mean.Same samples: up to 18 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Sweden national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | mean.Same samples: 5–48 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | mean.Same samples: 10–20 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 10–1,760 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawFood 2016 | UK retail2013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawFood et al. 2014 | UK retail outlets, 2013-20142013–2014basis not stated | below LOD. | ||
| Fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | mean.Same samples: 3–30 µg/kg (range) | ||
| Fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | range. | ||
| Fish, species not stated · fresh or rawLim et al. 2015 | Supermarkets and marketplaces in2010–2011basis not stated | mean.Same samples: 0.1–354 µg/kg (range) | ||
| Fish, species not stated · fresh or rawLim et al. 2015 | Supermarkets and marketplaces in2010–2011basis not stated | median. | ||
| Fish, species not stated · fresh or rawLim et al. 2015 | Supermarkets and marketplaces in2010–2011basis not stated | range. | ||
| Fish, species not stated · fresh or rawLoutfy et al. 2012 | 'All the samples were produced2007 | mean.Same samples: 420–2,100 µg/kg (range) | ||
| Fish, species not stated · fresh or rawLoutfy et al. 2012 | 'All the samples were produced2007 | range. | ||
| Fish, species not stated · fresh or rawOlmedo et al. 2013 | Granada, Spain2009–2010 | below LOD. | ||
| Fish, species not stated · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Fish, species not stated · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Fish, species not stated · fresh or rawScientific Research… 2020 | caldera near Sea Diamond wreck2019basis not stated | below LOD. | ||
| Fish, species not stated · fresh or rawSmolikova et al. 2016 | Brno City markets, Czech Republic2015–2016 | below LOD. | ||
| Fish, species not stated · fresh or rawtotal mercury (THg),… 2026 | Lake Vanajanselka, Finland1970–2002 | median. | ||
| Fish, species not stated · fresh or rawtotal mercury (THg),… 2026 | Northern Quark1970–2002 | below LOD. | ||
| Fish, species not stated · fresh or rawWang et al. 2019 | retail, Guangzhou, China2014–2017basis not stated | mean. | ||
| Fish, species not stated · fresh or rawWang et al. 2019 | retail, Guangzhou, China2014–2017basis not stated | median. | ||
30 findings · 7 studies · 6 spread figures folded in | ||||
| Herring · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | mean. | ||
| Grey mullet · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | mean. | ||
| Grey mullet · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | mean. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · smoked, dried, salted or fermentedVenant et al. 2025 | Lake Victoria, TanzaniaCollection date unreportedbasis not stated | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region AFRO2012dry weight | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region AFRO2013dry weight | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region WPRO2002–2008 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets in Ouagadougou2020basis not stated | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets in Ouagadougou2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Bobo Dioulasso2020basis not stated | median.Same samples: 220–3,200 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Bobo Dioulasso2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Cinkasse2020basis not stated | median.Same samples: up to 2,400 µg/kg (range maximum) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Cinkasse2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Dakola2020basis not stated | median.Same samples: up to 1,770 µg/kg (range maximum) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Dakola2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Niankologo2020basis not stated | median.Same samples: 200–2,600 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Niankologo2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Ouagadougou2020basis not stated | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Ouagadougou2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBrima et al. 2025 | various African countries2023–2024dry weight | mean.Same samples: 50–430 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBrima et al. 2025 | various African countries2023–2024dry weight | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean.Same samples: 450–620 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedFagbemi et al. 2023 | street vendors at three busy roadCollection date unreportedbasis not stated | mean. | ||
2 findings · 1 study | ||||
| Cod · fish oilWHO GEMS/Food | WHO region EURO2008–2015 | median. | ||
| Fish, species not stated · fish oilWHO GEMS/Food | WHO region EURO2011–2019 | median. | ||
41 findings · 10 studies · 6 spread figures folded in | ||||
| Cod · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean. | ||
| Cod · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | max. | ||
| Cod · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Cod · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Pollock and saithe · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Pollock and saithe · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Pollock and saithe · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Tilapia · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean.Same samples: 103–140 µg/kg (range) | ||
| Tilapia · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | range. | ||
| Carp and other cyprinids · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 9–15 µg/kg (range) | ||
| Carp and other cyprinids · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Catfish · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean.Same samples: 107–201 µg/kg (range) | ||
| Catfish · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | sample value. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2003–2019 | median. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2010–2017 | median. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region WPRO2009–2016 | median. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2003–2019 | median. | ||
| Fish, species not stated · fish productFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Fish, species not stated · fish productANSES 2026 | France retail2021–2022 | mean. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean. | ||
| Fish, species not stated · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | range. | ||
| Fish, species not stated · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 16–78 µg/kg (range) | ||
| Fish, species not stated · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Fish, species not stated · fish productEFSA 2010 | EU Member States and Norway2003–2008basis not stated | mean.Same samples: 290 µg/kg (maximum) | ||
| Fish, species not stated · fish productEFSA 2010 | EU Member States and Norway2003–2008basis not stated | mean. | ||
| Fish, species not stated · fish productEFSA 2010 | EU Member States and Norway2003–2008basis not stated | median. | ||
| Fish, species not stated · fish productEFSA 2010 | EU Member States and Norway2003–2008basis not stated | below LOD. | ||
| Fish, species not stated · fish productEFSA 2010 | EU Member States and Norway2003–2008basis not stated | max. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | mean.Same samples: 10–10 µg/kg (range) | ||
| Fish, species not stated · fish productEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | range. | ||
| Fish, species not stated · fish productKazimov et al. 2014 | Baku, AzerbaijanCollection date unreportedbasis not stated | max. | ||
| Fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
| Fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | below LOD. | ||
3 findings · 2 studies | ||||
| Fish, species not stated · fish sauceWHO GEMS/Food | WHO region EURO2005–2023 | median. | ||
| Fish, species not stated · fish sauceAbdullah 2009 | Fish sauce sample ACollection date unreportedbasis not stated | sample value. | ||
| Fish, species not stated · fish sauceAbdullah 2009 | Fish sauce sample BCollection date unreportedbasis not stated | sample value. | ||
86 findings · 12 studies · 6 spread figures folded in | ||||
| Tuna · cannedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedFood 2019 | Retail/takeaway purchases across2013–2014 | mean. | ||
| Tuna · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Tuna · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Tuna · cannedOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Tuna · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 790–7,080 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 310–1,870 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 370–990 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedUlusoy 2023 | label origin Holland; FAO area 672017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Iran2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Canada; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Seychelles2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Maldives2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Mauritius2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin The Ivory Coast2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Holland; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Spain2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Philippines2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Equator [Ecuador]2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin United Arab Emirates2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Algeria2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Argentina2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Brazil2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Equator [Ecuador]2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Morocco2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Portugal2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Thailand; FAO area 712017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Indonesia2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Tunisia2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Spain; FAO area 512017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Indonesia2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Italy2017–2019 | mean. | ||
| Tuna · cannedUlusoy 2023 | label origin Turkey2017–2019 | mean. | ||
| Mackerel · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Mackerel · cannedNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 950–1,500 µg/kg (range) | ||
| Mackerel · cannedNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Mackerel · cannedNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 1,100–1,900 µg/kg (range) | ||
| Mackerel · cannedNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Mackerel · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Herring · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Sardine and pilchard · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Sardine and pilchard · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Anchovy · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Salmon · cannedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Salmon · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Fish, species not stated · cannedWHO GEMS/Food | WHO region EURO2014–2023 | median. | ||
| Fish, species not stated · cannedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cannedFood 2016 | Major retailers, Dublin, Ireland2012–2014 | range. | ||
| Fish, species not stated · cannedSalahel et al. 2025 | randomly selected local markets2022basis not stated | mean.Same samples: 7–9 µg/kg (range) | ||
| Fish, species not stated · cannedSalahel et al. 2025 | randomly selected local markets2022basis not stated | range. | ||
41 findings · 8 studies · 2 spread figures folded in | ||||
| Tuna · cookedWHO GEMS/Food | WHO region European Union2007–2008 | median. | ||
| Tuna · cookedWHO GEMS/Food | WHO region WPRO2014 | median. | ||
| Horse mackerel, jacks and trevally · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Sardine and pilchard · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Sardine and pilchard · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Sardine and pilchard · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Shad, hilsa and other herrings · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Shad, hilsa and other herrings · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Shad, hilsa and other herrings · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Salmon · cookedWHO GEMS/Food | WHO region European Union2007–2009 | median. | ||
| Salmon · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Trout and char · cookedWHO GEMS/Food | WHO region European Union2002–2003 | median. | ||
| Cod · cookedWHO GEMS/Food | WHO region European Union2002–2003 | median. | ||
| Cod · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Cod · cookedWang et al. 2020 | Jilin Province, China2015–2016basis not stated | mean. | ||
| Cod · cookedWang et al. 2020 | other areas of Jilin Province2015–2016basis not stated | mean. | ||
| Cod · cookedWang et al. 2020 | Songhua River Basin area2015–2016basis not stated | mean. | ||
| Plaice, flounder, sole and turbot · cookedLiu et al. 2023 | Nanshan Market, Qingdao, ChinaCollection date unreportedbasis not stated | mean. | ||
| Plaice, flounder, sole and turbot · cookedLiu et al. 2023 | Nanshan Market, Qingdao, ChinaCollection date unreportedbasis not stated | mean. | ||
| Other marine fish · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Tilapia · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Carp and other cyprinids · cookedWang et al. 2020 | Jilin Province, China2015–2016basis not stated | mean. | ||
| Carp and other cyprinids · cookedWang et al. 2020 | other areas of Jilin Province2015–2016basis not stated | mean. | ||
| Carp and other cyprinids · cookedWang et al. 2020 | Songhua River Basin area2015–2016basis not stated | mean. | ||
| Marine fish, species not stated · cookedWHO GEMS/Food | WHO region AFRO2018 | median. | ||
| Marine fish, species not stated · cookedWHO GEMS/Food | WHO region WPRO2009 | median. | ||
| Marine fish, species not stated · cookedVentura et al. 2025 | retail2014–2016 | mean.Same samples: 809–14,000 µg/kg (range) | ||
| Marine fish, species not stated · cookedVentura et al. 2025 | retail2014–2016 | range. | ||
| Freshwater fish, species not stated · cookedWHO GEMS/Food | WHO region AFRO2018 | median. | ||
| Freshwater fish, species not stated · cookedVentura et al. 2025 | retail2014–2016 | mean.Same samples: 46–70 µg/kg (range) | ||
| Freshwater fish, species not stated · cookedVentura et al. 2025 | retail2014–2016 | range. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region AFRO2018 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region EURO2008–2015 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region European Union2007–2014 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region WPRO1998–2014 | median. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cookedFood 2019 | Retail/takeaway purchases across2013–2014 | mean. | ||
| Fish, species not stated · cookedReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Fish, species not stated · cookedVentura et al. 2025 | retail2014–2016 | mean. | ||
| Fish, species not stated · cookedWang et al. 2020 | Jilin Province, China2015–2016basis not stated | mean. | ||
584 findings · 62 studies · 176 spread figures folded in | ||||
| Tuna · fresh or rawWHO GEMS/Food | WHO region EURO2003–2023 | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region European Union2000–2014 | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region WPRO2000–2008 | median. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | mean.Same samples: 880–3,610 µg/kg (range) | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | geometric mean. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | range. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | mean.Same samples: 430–1,160 µg/kg (range) | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | geometric mean. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | range. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | mean.Same samples: 430–3,610 µg/kg (range) | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | geometric mean. | ||
| Tuna · fresh or rawBae et al. 2023 | Japanese restaurants2021basis not stated | range. | ||
| Tuna · fresh or rawBrooke et al. 1981 | NBS dried tunaCollection date unreporteddry weight | sample value. | ||
| Tuna · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Tuna · fresh or rawLehel et al. 2023 | Sri LankaCollection date unreported | mean.Same samples: 510–2,050 µg/kg (range) | ||
| Tuna · fresh or rawLehel et al. 2023 | Sri LankaCollection date unreported | range. | ||
| Tuna · fresh or rawMatsumoto-Tanibuchi et… 2019 | local market in JapanCollection date unreportedbasis not stated | mean. | ||
| Tuna · fresh or rawOlmedo et al. 2013 | Canary Islands, Spain2009–2010 | median. | ||
| Tuna · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Tuna · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Tuna · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Swordfish · fresh or rawWHO GEMS/Food | WHO region EURO2018 | median. | ||
| Swordfish · fresh or rawOlmedo et al. 2013 | Galicia, Spain2009–2010 | median. | ||
| Shark · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Shark · fresh or rawFalconer et al. 1983 | Aberdeen Bank fishing area1975–1982 | mean.Same samples: 1,900–3,800 µg/kg (range) | ||
| Shark · fresh or rawFalconer et al. 1983 | Aberdeen Bank fishing area1975–1982 | range. | ||
| Shark · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Shark · fresh or rawFattorini et al. 2006 | Tyrrhenian SeaCollection date unreporteddry weight | mean. | ||
| Shark · fresh or rawOlmedo et al. 2013 | Basque Country, Spain2009–2010 | median. | ||
| Shark · fresh or rawOlmedo et al. 2013 | Valencia, Spain2009–2010 | median. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Ray and skate · fresh or rawFalconer et al. 1983 | Aberdeen Bank fishing area1975–1982 | mean.Same samples: 9,100–31,800 µg/kg (range) | ||
| Ray and skate · fresh or rawFalconer et al. 1983 | Aberdeen Bank fishing area1975–1982 | range. | ||
| Ray and skate · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region EURO2003–2023 | median. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region European Union2000–2014 | median. | ||
| Mackerel · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Mackerel · fresh or rawEuropean et al. 2004 | Ireland national submission to1990–2002basis not stated | sample value. | ||
| Mackerel · fresh or rawFalconer et al. 1983 | Bergen Bank fishing area1975–1982 | mean.Same samples: 700–1,600 µg/kg (range) | ||
| Mackerel · fresh or rawFalconer et al. 1983 | Bergen Bank fishing area1975–1982 | range. | ||
| Mackerel · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | mean.Same samples: 400–1,700 µg/kg (range) | ||
| Mackerel · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | range. | ||
| Mackerel · fresh or rawFalconer et al. 1983 | Firth of Forth fishing area1975–1982 | mean.Same samples: 200–700 µg/kg (range) | ||
| Mackerel · fresh or rawFalconer et al. 1983 | Firth of Forth fishing area1975–1982 | range. | ||
| Mackerel · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Mackerel · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | mean.Same samples: 300–1,400 µg/kg (range) | ||
| Mackerel · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | range. | ||
| Mackerel · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Mackerel · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Mackerel · fresh or rawReinke et al. 1975 | Western AtlanticCollection date unreportedbasis not stated | mean. | ||
| Mackerel · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Mackerel · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Mackerel · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Mackerel · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| King and Spanish mackerel · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawFattorini et al. 2004 | Bahia, Cienfuegos Bay, Cuba2001dry weight | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawFattorini et al. 2004 | Corona, Cienfuegos Bay, Cuba2001dry weight | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawFattorini et al. 2006 | Cienfuegos Bay, CubaCollection date unreporteddry weight | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Horse mackerel, jacks and trevally · fresh or rawOlmedo et al. 2013 | Valencia, Spain2009–2010 | median. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Herring · fresh or rawWHO GEMS/Food | WHO region EURO2003–2023 | median. | ||
| Herring · fresh or rawWHO GEMS/Food | WHO region European Union2000–2014 | median. | ||
| Herring · fresh or rawBrooke et al. 1981 | HerringCollection date unreportedbasis not stated | sample value. | ||
| Herring · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 155–1,080 µg/kg (range) | ||
| Herring · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Herring · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | mean.Same samples: 1,000–2,400 µg/kg (range) | ||
| Herring · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | range. | ||
| Herring · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Herring · fresh or rawFalconer et al. 1983 | North Minch fishing area1975–1982 | mean.Same samples: 500–1,700 µg/kg (range) | ||
| Herring · fresh or rawFalconer et al. 1983 | North Minch fishing area1975–1982 | range. | ||
| Herring · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | mean.Same samples: 400–1,400 µg/kg (range) | ||
| Herring · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | range. | ||
| Herring · fresh or rawNorin et al. 1985 | FuruögrundCollection date unreported | mean. | ||
| Herring · fresh or rawNorin et al. 1985 | SkelleftebuktenCollection date unreported | mean. | ||
| Herring · fresh or rawReinke et al. 1975 | Western AtlanticCollection date unreportedbasis not stated | mean. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region EURO2004–2023 | median. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region European Union2000–2014 | median. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region WPRO2000–2002 | median. | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | northern sector2018 | mean.Same samples: 1,900–5,500 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | northern sector2018 | range. | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | southern sector2018 | mean.Same samples: 2,300–8,400 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | southern sector2018 | range. | ||
| Sardine and pilchard · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Sardine and pilchard · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Sardine and pilchard · fresh or rawMatsumoto-Tanibuchi et… 2019 | local market in JapanCollection date unreportedbasis not stated | mean. | ||
| Sardine and pilchard · fresh or rawMunoz et al. 1999 | local retail outletsCollection date unreporteddry weight | sample value. | ||
| Sardine and pilchard · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Sardine and pilchard · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Sardine and pilchard · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Sardine and pilchard · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Sprat · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 465–671 µg/kg (range) | ||
| Sprat · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Sprat · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | mean.Same samples: 800–2,200 µg/kg (range) | ||
| Sprat · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | range. | ||
| Sprat · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Anchovy · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Anchovy · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Anchovy · fresh or rawMunoz et al. 1999 | local retail outletsCollection date unreporteddry weight | sample value. | ||
| Anchovy · fresh or rawOlmedo et al. 2013 | Catalonia, Spain2009–2010 | median. | ||
| Anchovy · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Anchovy · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Anchovy · fresh or rawSimionov et al. 2023 | Fishing, Black Sea, BulgariaCollection date unreported | mean. | ||
| Shad, hilsa and other herrings · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Shad, hilsa and other herrings · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Shad, hilsa and other herrings · fresh or rawMatsumoto-Tanibuchi et… 2019 | local market in JapanCollection date unreportedbasis not stated | mean. | ||
| Shad, hilsa and other herrings · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean. | ||
| Shad, hilsa and other herrings · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 220–640 µg/kg (range) | ||
| Shad, hilsa and other herrings · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Shad, hilsa and other herrings · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 270–770 µg/kg (range) | ||
| Shad, hilsa and other herrings · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Shad, hilsa and other herrings · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 220–440 µg/kg (range) | ||
| Shad, hilsa and other herrings · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Shad, hilsa and other herrings · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 290–670 µg/kg (range) | ||
| Shad, hilsa and other herrings · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Shad, hilsa and other herrings · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 500–870 µg/kg (range) | ||
| Shad, hilsa and other herrings · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Shad, hilsa and other herrings · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 360–870 µg/kg (range) | ||
| Shad, hilsa and other herrings · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Shad, hilsa and other herrings · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region EURO2018–2023 | median. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region European Union2001 | median. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region WPRO1998–2005 | median. | ||
| Salmon · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 358–960 µg/kg (range) | ||
| Salmon · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Salmon · fresh or rawLuvonga et al. 2021 | river-based aquaculture facilityCollection date unreported | mean. | ||
| Salmon · fresh or rawLuvonga et al. 2021 | caught about 15 miles off theCollection date unreported | mean. | ||
| Salmon · fresh or rawOlmedo et al. 2013 | Norway2009–2010 | median. | ||
| Salmon · fresh or rawSimionov et al. 2023 | Aquaculture, NorwayCollection date unreported | mean. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region EURO2003–2023 | median. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region European Union2000–2014 | median. | ||
| Trout and char · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 579–1,520 µg/kg (range) | ||
| Trout and char · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Trout and char · fresh or rawGroleau et al. 2025 | Nunavik, Quebec, CanadaCollection date unreported | sample value. | ||
| Trout and char · fresh or rawLehel et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean.Same samples: 540–2,790 µg/kg (range) | ||
| Trout and char · fresh or rawLehel et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | range. | ||
| Trout and char · fresh or rawMatsumoto-Tanibuchi et… 2019 | local market in JapanCollection date unreportedbasis not stated | mean. | ||
| Trout and char · fresh or rawSimionov et al. 2023 | Aquaculture, RomaniaCollection date unreported | mean. | ||
| Trout and char · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Trout and char · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Trout and char · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Trout and char · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Whitefish and vendace · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 7–34 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Whitefish and vendace · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 44–103 µg/kg (range) | ||
| Whitefish and vendace · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region EURO2003–2023 | median. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region European Union2001–2014 | median. | ||
| Cod · fresh or rawFalconer et al. 1983 | Bergen Bank fishing area1975–1982 | mean.Same samples: 600–2,400 µg/kg (range) | ||
| Cod · fresh or rawFalconer et al. 1983 | Bergen Bank fishing area1975–1982 | range. | ||
| Cod · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | mean.Same samples: 700–18,600 µg/kg (range) | ||
| Cod · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | range. | ||
| Cod · fresh or rawFalconer et al. 1983 | Firth of Forth fishing area1975–1982 | mean.Same samples: 800–4,600 µg/kg (range) | ||
| Cod · fresh or rawFalconer et al. 1983 | Firth of Forth fishing area1975–1982 | range. | ||
| Cod · fresh or rawFalconer et al. 1983 | Ling Bank fishing area1975–1982 | mean.Same samples: 500–4,300 µg/kg (range) | ||
| Cod · fresh or rawFalconer et al. 1983 | Ling Bank fishing area1975–1982 | range. | ||
| Cod · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Cod · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | mean.Same samples: 400–2,000 µg/kg (range) | ||
| Cod · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | range. | ||
| Cod · fresh or rawOlmedo et al. 2013 | Atlantic Northeast2009–2010 | median. | ||
| Cod · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Haddock · fresh or rawBrooke et al. 1981 | HaddockCollection date unreportedbasis not stated | sample value. | ||
| Haddock · fresh or rawFalconer et al. 1983 | Bergen Bank fishing area1975–1982 | mean.Same samples: 1,100–5,700 µg/kg (range) | ||
| Haddock · fresh or rawFalconer et al. 1983 | Bergen Bank fishing area1975–1982 | range. | ||
| Haddock · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | mean.Same samples: 3,900–6,700 µg/kg (range) | ||
| Haddock · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | range. | ||
| Haddock · fresh or rawFalconer et al. 1983 | Firth of Forth fishing area1975–1982 | mean.Same samples: 2,200–4,100 µg/kg (range) | ||
| Haddock · fresh or rawFalconer et al. 1983 | Firth of Forth fishing area1975–1982 | range. | ||
| Haddock · fresh or rawFalconer et al. 1983 | Ling Bank fishing area1975–1982 | mean.Same samples: 1,400–6,700 µg/kg (range) | ||
| Haddock · fresh or rawFalconer et al. 1983 | Ling Bank fishing area1975–1982 | range. | ||
| Haddock · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Haddock · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | mean.Same samples: 1,100–2,400 µg/kg (range) | ||
| Haddock · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | range. | ||
| Haddock · fresh or rawReinke et al. 1975 | Western AtlanticCollection date unreportedbasis not stated | mean. | ||
| Pollock and saithe · fresh or rawFalconer et al. 1983 | Bergen Bank fishing area1975–1982 | mean.Same samples: 200–1,800 µg/kg (range) | ||
| Pollock and saithe · fresh or rawFalconer et al. 1983 | Bergen Bank fishing area1975–1982 | range. | ||
| Pollock and saithe · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | mean.Same samples: 600–1,300 µg/kg (range) | ||
| Pollock and saithe · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | range. | ||
| Pollock and saithe · fresh or rawFalconer et al. 1983 | Ling Bank fishing area1975–1982 | mean.Same samples: 500–3,500 µg/kg (range) | ||
| Pollock and saithe · fresh or rawFalconer et al. 1983 | Ling Bank fishing area1975–1982 | range. | ||
| Pollock and saithe · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Pollock and saithe · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | mean.Same samples: 400–1,000 µg/kg (range) | ||
| Pollock and saithe · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | range. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara, 8 stations2019 | mean.Same samples: 569–4,560 µg/kg (range) | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara, 8 stations2019 | range. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L12019 | mean. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L22019 | mean. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L32019 | mean. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L52019 | mean. | ||
| Whiting and blue whiting · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L72019 | mean. | ||
| Whiting and blue whiting · fresh or rawFalconer et al. 1983 | Bergen Bank fishing area1975–1982 | mean.Same samples: 800–2,600 µg/kg (range) | ||
| Whiting and blue whiting · fresh or rawFalconer et al. 1983 | Bergen Bank fishing area1975–1982 | range. | ||
| Whiting and blue whiting · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | mean.Same samples: 900–2,400 µg/kg (range) | ||
| Whiting and blue whiting · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | range. | ||
| Whiting and blue whiting · fresh or rawFalconer et al. 1983 | Firth of Forth fishing area1975–1982 | mean.Same samples: 1,000–1,900 µg/kg (range) | ||
| Whiting and blue whiting · fresh or rawFalconer et al. 1983 | Firth of Forth fishing area1975–1982 | range. | ||
| Whiting and blue whiting · fresh or rawFalconer et al. 1983 | Ling Bank fishing area1975–1982 | mean.Same samples: 800–2,800 µg/kg (range) | ||
| Whiting and blue whiting · fresh or rawFalconer et al. 1983 | Ling Bank fishing area1975–1982 | range. | ||
| Whiting and blue whiting · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Whiting and blue whiting · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | mean.Same samples: 600–1,200 µg/kg (range) | ||
| Whiting and blue whiting · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | range. | ||
| Whiting and blue whiting · fresh or rawOlmedo et al. 2013 | Galicia, Spain2009–2010 | median. | ||
| Hake · fresh or rawEuropean et al. 2004 | Italy national submission to SCOOP1990–2002basis not stated | mean.Same samples: 5,900–16,100 µg/kg (range) | ||
| Hake · fresh or rawEuropean et al. 2004 | Italy national submission to SCOOP1990–2002basis not stated | range. | ||
| Hake · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | mean.Same samples: 500–1,500 µg/kg (range) | ||
| Hake · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | range. | ||
| Hake · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Hake · fresh or rawOlmedo et al. 2013 | Valencia, Spain2009–2010 | median. | ||
| Hake · fresh or rawOlmedo et al. 2013 | Mauritania2009–2010 | median. | ||
| Hake · fresh or rawOlmedo et al. 2013 | Mauritania2009–2010 | median. | ||
| Hake · fresh or rawSimionov et al. 2023 | Spain; fishing area not specifiedCollection date unreported | mean. | ||
| Ling, tusk and other cod-like fish · fresh or rawFalconer et al. 1983 | Aberdeen Bank fishing area1975–1982 | mean.Same samples: 1,200–3,800 µg/kg (range) | ||
| Ling, tusk and other cod-like fish · fresh or rawFalconer et al. 1983 | Aberdeen Bank fishing area1975–1982 | range. | ||
| Ling, tusk and other cod-like fish · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Ling, tusk and other cod-like fish · fresh or rawFounder (2018) | Moscow consumer market, RussiaCollection date unreportedbasis not stated | sample value. | ||
| Ling, tusk and other cod-like fish · fresh or rawReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawBrooke et al. 1981 | PlaiceCollection date unreportedbasis not stated | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Aberdeen Bank fishing area1975–1982 | mean.Same samples: 2,500–11,600 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Aberdeen Bank fishing area1975–1982 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Aberdeen Bank fishing area1975–1982 | mean.Same samples: 6,800–19,500 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Aberdeen Bank fishing area1975–1982 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Firth of Forth fishing area1975–1982 | mean.Same samples: 14,000–16,000 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Firth of Forth fishing area1975–1982 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | North Minch fishing area1975–1982 | mean.Same samples: 1,200–3,400 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | North Minch fishing area1975–1982 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Aberdeen Bank fishing area1975–1982 | mean.Same samples: 4,000–11,200 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Aberdeen Bank fishing area1975–1982 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Clyde1975–1982 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Bergen Bank fishing area1975–1982 | mean.Same samples: 6,700–27,500 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Bergen Bank fishing area1975–1982 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Clyde1975–1982 | max. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | mean.Same samples: 5,600–14,400 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Firth of Forth fishing area1975–1982 | mean.Same samples: 1,000–8,000 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Firth of Forth fishing area1975–1982 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Flamborough1975–1982 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | German Bight1975–1982 | max. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | German Bight1975–1982 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Ling Bank fishing area1975–1982 | mean.Same samples: 9,500–89,900 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Ling Bank fishing area1975–1982 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Ling Bank1975–1982 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Moray Firth fishing area1975–1982 | mean.Same samples: 3,300–41,300 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Moray Firth fishing area1975–1982 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Moray Firth1975–1982 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | mean.Same samples: 1,500–3,100 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Bergen Bank fishing area1975–1982 | mean.Same samples: 6,800–28,200 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Bergen Bank fishing area1975–1982 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | mean.Same samples: 8,100–23,500 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Clyde fishing area1975–1982 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Ling Bank fishing area1975–1982 | mean.Same samples: 4,600–44,200 µg/kg (range) | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Ling Bank fishing area1975–1982 | range. | ||
| Plaice, flounder, sole and turbot · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawOlmedo et al. 2013 | Morocco2009–2010 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Halibut · fresh or rawFounder (2018) | Moscow consumer market, RussiaCollection date unreportedbasis not stated | sample value. | ||
| Halibut · fresh or rawKaise et al. 1988 | commercially available, Japan1987basis not stated | sample value. | ||
| Halibut · fresh or rawReinke et al. 1975 | Western AtlanticCollection date unreportedbasis not stated | mean. | ||
| Sea bass and barramundi · fresh or rawBalzani et al. 2026 | Dalyan Lake2021dry weight | mean. | ||
| Sea bass and barramundi · fresh or rawCirillo et al. 2010 | local fish markets2007 | median. | ||
| Sea bass and barramundi · fresh or rawFounder (2018) | Moscow consumer market, RussiaCollection date unreportedbasis not stated | sample value. | ||
| Sea bass and barramundi · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Sea bass and barramundi · fresh or rawLevent 2022 | Sinop fish markets, Turkey2020 | mean. | ||
| Sea bass and barramundi · fresh or rawLevent 2022 | Sinop fish markets, Turkey2020 | mean. | ||
| Sea bass and barramundi · fresh or rawLevent 2022 | Sinop fish markets, Turkey2020 | mean. | ||
| Sea bass and barramundi · fresh or rawOlmedo et al. 2013 | Murcia, Spain2009–2010 | median. | ||
| Sea bass and barramundi · fresh or rawRay et al. 2025 | coastal and inland watersCollection date unreporteddry weight | mean. | ||
| Sea bass and barramundi · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawBalzani et al. 2026 | Dalyan Lake2021dry weight | mean. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 4,350–5,090 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 2,730–5,020 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Sea bream and porgies · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Sea bream and porgies · fresh or rawOlmedo et al. 2013 | Murcia, Spain2009–2010 | median. | ||
| Sea bream and porgies · fresh or rawSimionov et al. 2023 | Aquaculture, GreeceCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Sea bream and porgies · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Red mullet and goatfish · fresh or rawCirillo et al. 2010 | local fish markets2007 | median. | ||
| Red mullet and goatfish · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Red mullet and goatfish · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 8,100–11,800 µg/kg (range) | ||
| Red mullet and goatfish · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Red mullet and goatfish · fresh or rawOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Grey mullet · fresh or rawBakhshalizadeh et al. 2023 | Southern Caspian SeaCollection date unreportedbasis not stated | median. | ||
| Grey mullet · fresh or rawBalzani et al. 2026 | Dalyan Lake2021dry weight | mean. | ||
| Grey mullet · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Grey mullet · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Grey mullet · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | sample value. | ||
| Grey mullet · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Grey mullet · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Grey mullet · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Snapper · fresh or rawFattorini et al. 2004 | Bahia, Cienfuegos Bay, Cuba2001dry weight | mean. | ||
| Snapper · fresh or rawFattorini et al. 2004 | Corona, Cienfuegos Bay, Cuba2001dry weight | mean. | ||
| Snapper · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Snapper · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Grouper · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Grouper · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Grouper · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Croaker and drum · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Croaker and drum · fresh or rawFattorini et al. 2004 | Cuatro Boyas, Cienfuegos Bay, Cuba2001dry weight | mean. | ||
| Croaker and drum · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Croaker and drum · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Emperors and grunts · fresh or rawFattorini et al. 2004 | Bahia, Cienfuegos Bay, Cuba2001dry weight | mean. | ||
| Emperors and grunts · fresh or rawFattorini et al. 2006 | Cienfuegos Bay, CubaCollection date unreporteddry weight | mean. | ||
| Emperors and grunts · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Emperors and grunts · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Emperors and grunts · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Emperors and grunts · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Pomfret · fresh or rawAlongkote et al. 2025 | not stated2025 | mean. | ||
| Pomfret · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Pomfret · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Pomfret · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Hairtail and cutlassfish · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Barracuda · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Barracuda · fresh or rawFattorini et al. 2006 | Ionian SeaCollection date unreporteddry weight | mean. | ||
| Barracuda · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Barracuda · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Barracuda · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Barracuda · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Scorpionfish and rockfish · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Anglerfish and monkfish · fresh or rawFalconer et al. 1983 | Scottish waters1975–1982 | mean. | ||
| Anglerfish and monkfish · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | mean.Same samples: 3,700–17,500 µg/kg (range) | ||
| Anglerfish and monkfish · fresh or rawFalconer et al. 1983 | Shetland fishing area1975–1982 | range. | ||
| Anglerfish and monkfish · fresh or rawOlmedo et al. 2013 | Mauritania2009–2010 | median. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara, 8 stations2019 | mean.Same samples: 135–1,350 µg/kg (range) | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara, 8 stations2019 | range. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L12019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L32019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L42019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L52019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L62019 | mean. | ||
| Gurnard · fresh or rawBioaccumulation of… 2025 | Sea of Marmara station L82019 | mean. | ||
| Gurnard · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sturgeon · fresh or rawBondareva et al. 2024 | aquaculture farmCollection date unreporteddry weight | mean. | ||
| Sturgeon · fresh or rawBondareva et al. 2024 | aquaculture farmCollection date unreporteddry weight | mean. | ||
| Sturgeon · fresh or rawBondareva et al. 2024 | aquaculture farmCollection date unreporteddry weight | mean. | ||
| Sturgeon · fresh or rawBondareva et al. 2024 | aquaculture farmCollection date unreporteddry weight | mean. | ||
| Sturgeon · fresh or rawBondareva et al. 2024 | aquaculture farmCollection date unreporteddry weight | mean. | ||
| Sturgeon · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Sturgeon · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawAlongkote et al. 2025 | not stated2025 | mean. | ||
| Other marine fish · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Other marine fish · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Other marine fish · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Other marine fish · fresh or rawFattorini et al. 2004 | Corona, Cienfuegos Bay, Cuba2001dry weight | mean. | ||
| Other marine fish · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Other marine fish · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawNorin et al. 1985 | FuruögrundCollection date unreported | mean. | ||
| Other marine fish · fresh or rawNorin et al. 1985 | SkelleftebuktenCollection date unreported | mean. | ||
| Other marine fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean. | ||
| Other marine fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 480–1,480 µg/kg (range) | ||
| Other marine fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Other marine fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 440–1,470 µg/kg (range) | ||
| Other marine fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Other marine fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 440–660 µg/kg (range) | ||
| Other marine fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Other marine fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 770–1,080 µg/kg (range) | ||
| Other marine fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Other marine fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 990–1,670 µg/kg (range) | ||
| Other marine fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Other marine fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 440–1,670 µg/kg (range) | ||
| Other marine fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Other marine fish · fresh or rawRay et al. 2025 | coastal and inland watersCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawReksten et al. 2021 | Bangladeshi waters, Bay of Bengal2018 | mean. | ||
| Other marine fish · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Tilapia · fresh or rawEgbe et al. 2023 | Lake Barombi KottoCollection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | mean.Same samples: 10–2,100 µg/kg (range) | ||
| Tilapia · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | range. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Lake zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Tilapia · fresh or rawRay et al. 2025 | coastal and inland watersCollection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Tilapia · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawWHO GEMS/Food | WHO region EURO2018–2022 | median. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Amarat reservoir2022basis not stated | mean.Same samples: 5–40 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Amarat reservoir2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Khawd reservoir2022basis not stated | mean.Same samples: 3–12 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Khawd reservoir2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Surur area2022basis not stated | mean.Same samples: 5–60 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Surur area2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 21–52 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | below LOD. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNorin et al. 1985 | Lake BodaträskCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawNorin et al. 1985 | Lakes Gäddträsk and SteningsträskCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 200–700 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 250–690 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 200–420 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 330–550 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 400–760 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 260–760 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 170–520 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 120–400 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 120–280 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 200–440 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 280–540 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 120–540 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 210–620 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 170–780 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 170–320 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 290–580 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 490–780 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 190–740 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 290–750 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 380–850 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 290–650 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 470–770 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 530–870 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 390–870 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Aquaculture, HungaryCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube Delta, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSubhanullah et al. 2024 | Khall2021–2022Fish product as reported, mg/L | sample value. | ||
| Carp and other cyprinids · fresh or rawSubhanullah et al. 2024 | Timergara2021–2022Fish product as reported, mg/L | sample value. | ||
| Carp and other cyprinids · fresh or rawSubhanullah et al. 2024 | Wari2021–2022basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Faro, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Itaituba, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Porto TrombetasCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | mean.Same samples: 40–210 µg/kg (range) | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | range. | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | mean.Same samples: 40–310 µg/kg (range) | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | range. | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Nandail river reachCollection date unreportedbasis not stated | mean.Same samples: 30–60 µg/kg (range) | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Nandail river reachCollection date unreportedbasis not stated | range. | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | mean.Same samples: 250–750 µg/kg (range) | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | range. | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | mean.Same samples: 140–470 µg/kg (range) | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | range. | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | mean.Same samples: 90–310 µg/kg (range) | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | range. | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | mean.Same samples: 90–250 µg/kg (range) | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | range. | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Nandail river reachCollection date unreportedbasis not stated | mean.Same samples: 70–280 µg/kg (range) | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Nandail river reachCollection date unreportedbasis not stated | range. | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | mean.Same samples: 120–310 µg/kg (range) | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | range. | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | mean.Same samples: 240–640 µg/kg (range) | ||
| Catfish · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | range. | ||
| Catfish · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | mean.Same samples: 10–7,100 µg/kg (range) | ||
| Catfish · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | range. | ||
| Catfish · fresh or rawOlmedo et al. 2013 | Vietnam2009–2010 | median. | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean. | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 300–1,110 µg/kg (range) | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 280–1,160 µg/kg (range) | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 280–540 µg/kg (range) | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 470–850 µg/kg (range) | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 800–1,170 µg/kg (range) | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 380–1,170 µg/kg (range) | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean. | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 230–960 µg/kg (range) | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 300–890 µg/kg (range) | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 230–580 µg/kg (range) | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 310–760 µg/kg (range) | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 530–1,030 µg/kg (range) | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 330–1,030 µg/kg (range) | ||
| Catfish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Catfish · fresh or rawSimionov et al. 2023 | Aquaculture, VietnamCollection date unreported | mean. | ||
| Catfish · fresh or rawSimionov et al. 2023 | Fishing, Danube Delta, RomaniaCollection date unreported | mean. | ||
| Catfish · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | below LOD. | ||
| Catfish · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Pike · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 22–170 µg/kg (range) | ||
| Pike · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Pike · fresh or rawNorin et al. 1985 | Lake BodaträskCollection date unreported | mean. | ||
| Pike · fresh or rawNorin et al. 1985 | FuruögrundCollection date unreported | mean. | ||
| Pike · fresh or rawNorin et al. 1985 | Lakes Gäddträsk and SteningsträskCollection date unreported | mean. | ||
| Pike · fresh or rawNorin et al. 1985 | SkelleftebuktenCollection date unreported | mean. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 10–288 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 9–223 µg/kg (range) | ||
| Perch, walleye and zander · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Perch, walleye and zander · fresh or rawMaikanov et al. 2020 | Lakes of the Shuchinsk-BurabayCollection date unreportedbasis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawNorin et al. 1985 | Lake BodaträskCollection date unreported | mean. | ||
| Perch, walleye and zander · fresh or rawNorin et al. 1985 | FuruögrundCollection date unreported | mean. | ||
| Perch, walleye and zander · fresh or rawNorin et al. 1985 | Lakes Gäddträsk and SteningsträskCollection date unreported | mean. | ||
| Perch, walleye and zander · fresh or rawNorin et al. 1985 | SkelleftebuktenCollection date unreported | mean. | ||
| Perch, walleye and zander · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | Valdeazogues River transectCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | Castilseras reservoirCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | El Entredicho open pit lakeCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | La Colada reservoirCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PLPCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PPACollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PPMCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PTHCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawHull et al. 2023 | Lake Killarney2019–2021basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawHull et al. 2023 | Angle Lake2019–2021basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawHull et al. 2023 | Steel Lake2019–2021basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawHull et al. 2023 | Bonney Lake2019–2021basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawHull et al. 2023 | Pine Lake2019–2021basis not stated | mean. | ||
| Black bass and sunfish · fresh or rawSimionov et al. 2023 | Aquaculture, ItalyCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Faro, western Pará, BrazilCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Itaituba, western Pará, BrazilCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Porto TrombetasCollection date unreported | mean. | ||
| Other cichlids · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | mean. | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | mean.Same samples: 150–420 µg/kg (range) | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | range. | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | mean.Same samples: 140–290 µg/kg (range) | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | range. | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Nandail river reachCollection date unreportedbasis not stated | mean.Same samples: 40–180 µg/kg (range) | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Nandail river reachCollection date unreportedbasis not stated | range. | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | mean.Same samples: 80–250 µg/kg (range) | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | range. | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | mean.Same samples: 90–400 µg/kg (range) | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | range. | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | mean.Same samples: 140–410 µg/kg (range) | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | range. | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | mean.Same samples: 40–510 µg/kg (range) | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | range. | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Nandail river reachCollection date unreportedbasis not stated | mean.Same samples: 70–410 µg/kg (range) | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Nandail river reachCollection date unreportedbasis not stated | range. | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | mean.Same samples: 180–470 µg/kg (range) | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | range. | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | mean.Same samples: 80–310 µg/kg (range) | ||
| Snakehead · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | range. | ||
| Snakehead · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | mean.Same samples: 20–150 µg/kg (range) | ||
| Snakehead · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | range. | ||
| Snakehead · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Faro, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Itaituba, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Juruti, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawAlbuquerque et al. 2026 | Santarém, western Pará, BrazilCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | mean.Same samples: 140–560 µg/kg (range) | ||
| Other freshwater fish · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | range. | ||
| Other freshwater fish · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | mean.Same samples: 190–340 µg/kg (range) | ||
| Other freshwater fish · fresh or rawArsenic Contamination… 2022 | Jamuna river reachCollection date unreportedbasis not stated | range. | ||
| Other freshwater fish · fresh or rawArsenic Contamination… 2022 | Nandail river reachCollection date unreportedbasis not stated | mean.Same samples: 10–90 µg/kg (range) | ||
| Other freshwater fish · fresh or rawArsenic Contamination… 2022 | Nandail river reachCollection date unreportedbasis not stated | range. | ||
| Other freshwater fish · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | mean.Same samples: 140–280 µg/kg (range) | ||
| Other freshwater fish · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | range. | ||
| Other freshwater fish · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | mean.Same samples: 180–400 µg/kg (range) | ||
| Other freshwater fish · fresh or rawArsenic Contamination… 2022 | Tulshiganga river reachCollection date unreportedbasis not stated | range. | ||
| Other freshwater fish · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | mean.Same samples: 27–149 µg/kg (range) | ||
| Other freshwater fish · fresh or rawEuropean et al. 2004 | Finland national submission to1990–2002basis not stated | range. | ||
| Other freshwater fish · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Other freshwater fish · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Other freshwater fish · fresh or rawNorin et al. 1985 | FuruögrundCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawNorin et al. 1985 | SkelleftebuktenCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawOlmedo et al. 2013 | Tanzania2009–2010 | median. | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean. | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 370–1,050 µg/kg (range) | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 490–1,170 µg/kg (range) | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 370–730 µg/kg (range) | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 600–850 µg/kg (range) | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 790–1,170 µg/kg (range) | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 540–1,100 µg/kg (range) | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean. | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 420–1,060 µg/kg (range) | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 390–1,150 µg/kg (range) | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 360–550 µg/kg (range) | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 650–870 µg/kg (range) | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | mean.Same samples: 760–1,150 µg/kg (range) | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean.Same samples: 360–1,060 µg/kg (range) | ||
| Other freshwater fish · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | range. | ||
| Other freshwater fish · fresh or rawSirisangarunroj et al. 2023 | three local fish markets in/nearCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2014–2024 | median. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region WPRO2009 | median. | ||
| Marine fish, species not stated · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | range. | ||
| Marine fish, species not stated · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | mean.Same samples: up to 231 µg/kg (range maximum) | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | median. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | range. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | mean.Same samples: 12–212 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | median. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | range. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | mean.Same samples: 12–310 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | median. | ||
| Marine fish, species not stated · fresh or rawCirillo et al. 2010 | local fish markets2007 | range. | ||
| Marine fish, species not stated · fresh or rawFattorini et al. 2006 | Cienfuegos Bay and MediterraneanCollection date unreporteddry weight | range. | ||
| Marine fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | mean.Same samples: 232–10,300 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | range. | ||
| Marine fish, species not stated · fresh or rawReksten et al. 2020 | Angolan coast2017 | mean. | ||
| Marine fish, species not stated · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2014–2023 | median. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2018–2022 | median. | ||
| Freshwater fish, species not stated · fresh or rawFish (2026) | Lakes Burtnieks2024–2025basis not stated | below LOD. | ||
| Freshwater fish, species not stated · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean. | ||
| Freshwater fish, species not stated · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean. | ||
| Freshwater fish, species not stated · fresh or rawPaul et al. 2025 | Lower Meghna River2022–2023basis not stated | mean. | ||
| Freshwater fish, species not stated · fresh or rawPaul et al. 2025 | Lower Meghna River, Bangladesh2022–2023basis not stated | range. | ||
| Freshwater fish, species not stated · fresh or rawRusko et al. 2026 | five Latvian inland lakes pooled2024–2025 | below LOD. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2014–2023 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2003–2023 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region European Union2000–2014 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2011–2017 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region WPRO1998–2008 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2015–2022 | median. | ||
| Fish, species not stated · fresh or rawChen et al. 2025 | Chongqing retail outlets2017–2021basis not stated | mean. | ||
| Fish, species not stated · fresh or rawChen et al. 2025 | Chongqing retail outlets2017–2021basis not stated | mean. | ||
| Fish, species not stated · fresh or rawChen et al. 2025 | Chongqing retail outlets2017–2021basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2009 | EFSA call for data2003–2008basis not stated | median.Same samples: 195,000 µg/kg (maximum) | ||
| Fish, species not stated · fresh or rawEFSA 2009 | EFSA call for data2003–2008basis not stated | max. | ||
| Fish, species not stated · fresh or rawEFSA 2009 | EFSA call for data2003–2008basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2009 | EFSA call for data2003–2008basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Belgium national submission to1990–2002basis not stated | mean.Same samples: 513–132,000 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Belgium national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Denmark national submission to1990–2002basis not stated | mean.Same samples: 140–11,500 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Denmark national submission to1990–2002basis not stated | median. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Denmark national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | France national submission to1990–2002basis not stated | mean.Same samples: 680–23,000 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | France national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Germany national submission to1990–2002basis not stated | mean.Same samples: up to 23,000 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Germany national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Sweden national submission to1990–2002basis not stated | mean.Same samples: 590–17,000 µg/kg (range); 170–1,000 µg/kg (range); 18–210 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Sweden national submission to1990–2002basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Sweden national submission to1990–2002basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Sweden national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Sweden national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Sweden national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | mean.Same samples: 1,260–8,070 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | mean.Same samples: 280–18,000 µg/kg (range) | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | median. | ||
| Fish, species not stated · fresh or rawEuropean et al. 2004 | Greece national submission to1990–2002basis not stated | range. | ||
| Fish, species not stated · fresh or rawFood 2016 | UK retail2013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawFood et al. 2014 | UK retail outlets, 2013-20142013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | mean.Same samples: 37–398 µg/kg (range) | ||
| Fish, species not stated · fresh or rawKim et al. 2023 | grocery stores and markets in2021basis not stated | range. | ||
| Fish, species not stated · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
| Fish, species not stated · fresh or rawReksten et al. 2021 | Sri Lankan waters, Bay of Bengal2018 | mean. | ||
1 finding · 1 study | ||||
| Cod · fish oilWHO GEMS/Food | WHO region EURO2008–2010 | median. | ||
33 findings · 8 studies · 22 spread figures folded in | ||||
| Cod · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean.Same samples: 582–1,110 µg/kg (range) | ||
| Cod · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | range. | ||
| Cod · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 330–500 µg/kg (range) | ||
| Cod · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Cod · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 310–550 µg/kg (range) | ||
| Cod · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Pollock and saithe · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 790–1,100 µg/kg (range) | ||
| Pollock and saithe · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Pollock and saithe · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | sample value. | ||
| Pollock and saithe · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | sample value. | ||
| Tilapia · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean.Same samples: 100–710 µg/kg (range) | ||
| Tilapia · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | range. | ||
| Catfish · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean.Same samples: 212–640 µg/kg (range) | ||
| Catfish · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 720–1,700 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 670–3,900 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 750–7,500 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 730–4,200 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 660–4,300 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 860–5,100 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 600–1,400 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 660–1,300 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 280–490 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 310–2,400 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 270–1,800 µg/kg (range) | ||
| Marine fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2007–2015 | median. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region WPRO2009 | median. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2014–2023 | median. | ||
| Fish, species not stated · fish productFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean.Same samples: 100–1,110 µg/kg (range) | ||
| Fish, species not stated · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | range. | ||
| Fish, species not stated · fish productEFSA 2009 | EFSA call for data2003–2008basis not stated | median.Same samples: 20,200 µg/kg (maximum) | ||
| Fish, species not stated · fish productEFSA 2009 | EFSA call for data2003–2008basis not stated | max. | ||
| Fish, species not stated · fish productEFSA 2009 | EFSA call for data2003–2008basis not stated | mean. | ||
| Fish, species not stated · fish productEFSA 2009 | EFSA call for data2003–2008basis not stated | mean. | ||
| Fish, species not stated · fish productEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | mean.Same samples: 3,900–6,100 µg/kg (range) | ||
| Fish, species not stated · fish productEuropean et al. 2004 | United Kingdom national submission1990–2002basis not stated | range. | ||
| Fish, species not stated · fish productFood 2019 | Retail/takeaway purchases across2013–2014 | mean. | ||
| Fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 280–1,000 µg/kg (range) | ||
| Fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
| Fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | mean.Same samples: 600–1,200 µg/kg (range) | ||
| Fish, species not stated · fish productNaess et al. 2020 | Norwegian retail market2015–2018 | range. | ||
8 findings · 3 studies | ||||
| Fish, species not stated · fish sauceWHO GEMS/Food | WHO region EURO2023 | median. | ||
| Fish, species not stated · fish sauceMatsumoto-Tanibuchi et… 2019 | local market in JapanCollection date unreported | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
5 findings · 2 studies · 1 spread figure folded in | ||||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region EURO2014–2018 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region WPRO2001–2002 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region WPRO2015 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region EURO2015–2023 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBrima et al. 2025 | various African countries2023–2024dry weight | mean.Same samples: 100–19,300 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBrima et al. 2025 | various African countries2023–2024dry weight | range. | ||
6 findings · 5 studies | ||||
| Tuna · cannedFood 2011 | Australian state/territory2008 | not detected. | ||
| Tuna · cannedFood 2019 | Retail/takeaway purchases across2013–2014 | not detected. | ||
| Salmon · cannedBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Fish, species not stated · cannedWHO GEMS/Food | WHO region EURO2015–2023 | median. | ||
| Fish, species not stated · cannedBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Fish, species not stated · cannedFood 2016 | Major retailers, Dublin, Ireland2012–2014 | range. | ||
29 findings · 6 studies · 10 spread figures folded in | ||||
| Tuna · cookedWHO GEMS/Food | WHO region WPRO2010–2022 | median. | ||
| Tuna · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 3–9 µg/kg (range) | ||
| Tuna · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | range. | ||
| Mackerel · cookedWHO GEMS/Food | WHO region WPRO2022 | median. | ||
| Sardine and pilchard · cookedWHO GEMS/Food | WHO region WPRO2022 | median. | ||
| Salmon · cookedWHO GEMS/Food | WHO region WPRO2022 | median. | ||
| Salmon · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 4–10 µg/kg (range) | ||
| Salmon · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | range. | ||
| Plaice, flounder, sole and turbot · cookedWHO GEMS/Food | WHO region WPRO2010–2011 | median. | ||
| Plaice, flounder, sole and turbot · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 5 µg/kg (range maximum) | ||
| Plaice, flounder, sole and turbot · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | range. | ||
| Plaice, flounder, sole and turbot · cookedLiu et al. 2023 | Nanshan Market, Qingdao, ChinaCollection date unreportedbasis not stated | mean. | ||
| Plaice, flounder, sole and turbot · cookedLiu et al. 2023 | Nanshan Market, Qingdao, ChinaCollection date unreportedbasis not stated | mean. | ||
| Grey mullet · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 9–14 µg/kg (range) | ||
| Grey mullet · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | range. | ||
| Grouper · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 13–24 µg/kg (range) | ||
| Grouper · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | range. | ||
| Croaker and drum · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 6–55 µg/kg (range) | ||
| Croaker and drum · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | range. | ||
| Pomfret · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 15–21 µg/kg (range) | ||
| Pomfret · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | range. | ||
| Sturgeon · cookedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | not detected. | ||
| Sturgeon · cookedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | not detected. | ||
| Other marine fish · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 12–24 µg/kg (range) | ||
| Other marine fish · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other marine fish · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 14–30 µg/kg (range) | ||
| Other marine fish · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | range. | ||
| Carp and other cyprinids · cookedWHO GEMS/Food | WHO region WPRO2010–2011 | median. | ||
| Carp and other cyprinids · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 4–6 µg/kg (range) | ||
| Carp and other cyprinids · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | range. | ||
| Carp and other cyprinids · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Other freshwater fish · cookedCentre 2012 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Bream (species group not stated) · cookedWHO GEMS/Food | WHO region WPRO2010 | median. | ||
| Marine fish, species not stated · cookedWHO GEMS/Food | WHO region WPRO2020–2022 | median. | ||
| Freshwater fish, species not stated · cookedWHO GEMS/Food | WHO region WPRO2022 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region WPRO1998–2014 | median. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cookedFood 2019 | Retail/takeaway purchases across2013–2014 | not detected. | ||
168 findings · 20 studies | ||||
| Tuna · fresh or rawWHO GEMS/Food | WHO region EURO2003–2023 | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region PAHO2018–2020dry weight | median. | ||
| Tuna · fresh or rawWHO GEMS/Food | WHO region WPRO2000–2022 | median. | ||
| Tuna · fresh or rawBrooke et al. 1981 | NBS dried tunaCollection date unreporteddry weight | sample value. | ||
| Tuna · fresh or rawBrooke et al. 1981 | NBS dried tunaCollection date unreporteddry weight | sample value. | ||
| Tuna · fresh or rawBrooke et al. 1981 | NBS dried tunaCollection date unreporteddry weight | sample value. | ||
| Tuna · fresh or rawBrooke et al. 1981 | NBS dried tunaCollection date unreporteddry weight | sample value. | ||
| Tuna · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Tuna · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Tuna · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Tuna · fresh or rawMatsumoto-Tanibuchi et… 2019 | local market in JapanCollection date unreportedbasis not stated | below LOD. | ||
| Shark · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region EURO2004–2023 | median. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region PAHO2018–2020dry weight | median. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region WPRO2020–2024 | median. | ||
| Mackerel · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Mackerel · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Mackerel · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Mackerel · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Mackerel · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Mackerel · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Mackerel · fresh or rawReinke et al. 1975 | Western AtlanticCollection date unreportedbasis not stated | below LOD. | ||
| Horse mackerel, jacks and trevally · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Horse mackerel, jacks and trevally · fresh or rawFattorini et al. 2004 | Bahia, Cienfuegos Bay, Cuba2001dry weight | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Herring · fresh or rawWHO GEMS/Food | WHO region EURO2003–2023 | median. | ||
| Herring · fresh or rawWHO GEMS/Food | WHO region PAHO2018–2020dry weight | median. | ||
| Herring · fresh or rawBrooke et al. 1981 | HerringCollection date unreportedbasis not stated | sample value. | ||
| Herring · fresh or rawBrooke et al. 1981 | HerringCollection date unreportedbasis not stated | sample value. | ||
| Herring · fresh or rawBrooke et al. 1981 | HerringCollection date unreportedbasis not stated | sample value. | ||
| Herring · fresh or rawBrooke et al. 1981 | HerringCollection date unreportedbasis not stated | sample value. | ||
| Herring · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Herring · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Herring · fresh or rawNorin et al. 1985 | FuruögrundCollection date unreported | sample value. | ||
| Herring · fresh or rawNorin et al. 1985 | FuruögrundCollection date unreported | sample value. | ||
| Herring · fresh or rawNorin et al. 1985 | SkelleftebuktenCollection date unreported | sample value. | ||
| Herring · fresh or rawNorin et al. 1985 | SkelleftebuktenCollection date unreported | sample value. | ||
| Herring · fresh or rawReinke et al. 1975 | Western AtlanticCollection date unreportedbasis not stated | below LOD. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region EURO2004–2023 | median. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region WPRO2020–2024 | median. | ||
| Sardine and pilchard · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Sardine and pilchard · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Sardine and pilchard · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Sardine and pilchard · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Sardine and pilchard · fresh or rawMatsumoto-Tanibuchi et… 2019 | local market in JapanCollection date unreportedbasis not stated | below LOD. | ||
| Sardine and pilchard · fresh or rawMunoz et al. 1999 | local retail outletsCollection date unreporteddry weight | sample value. | ||
| Sardine and pilchard · fresh or rawMunoz et al. 1999 | local retail outletsCollection date unreporteddry weight | sample value. | ||
| Sardine and pilchard · fresh or rawMunoz et al. 1999 | Sardine precision test dry massCollection date unreporteddry weight | mean. | ||
| Sardine and pilchard · fresh or rawMunoz et al. 1999 | Sardine precision test fresh massCollection date unreported | mean. | ||
| Anchovy · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Anchovy · fresh or rawMunoz et al. 1999 | local retail outletsCollection date unreporteddry weight | sample value. | ||
| Anchovy · fresh or rawMunoz et al. 1999 | local retail outletsCollection date unreporteddry weight | sample value. | ||
| Shad, hilsa and other herrings · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Shad, hilsa and other herrings · fresh or rawMatsumoto-Tanibuchi et… 2019 | local market in JapanCollection date unreportedbasis not stated | below LOD. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region PAHO2018–2020dry weight | median. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region WPRO1998–2024 | median. | ||
| Salmon · fresh or rawLuvonga et al. 2021 | river-based aquaculture facilityCollection date unreported | not detected. | ||
| Salmon · fresh or rawLuvonga et al. 2021 | caught about 15 miles off theCollection date unreported | not detected. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region EURO2003–2023 | median. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region PAHO2020dry weight | median. | ||
| Trout and char · fresh or rawMatsumoto-Tanibuchi et… 2019 | local market in JapanCollection date unreportedbasis not stated | below LOD. | ||
| Trout and char · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Trout and char · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region EURO2003–2023 | median. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region PAHO2020dry weight | median. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region WPRO2021 | median. | ||
| Haddock · fresh or rawBrooke et al. 1981 | HaddockCollection date unreportedbasis not stated | sample value. | ||
| Haddock · fresh or rawBrooke et al. 1981 | HaddockCollection date unreportedbasis not stated | sample value. | ||
| Haddock · fresh or rawBrooke et al. 1981 | HaddockCollection date unreportedbasis not stated | sample value. | ||
| Haddock · fresh or rawBrooke et al. 1981 | HaddockCollection date unreportedbasis not stated | sample value. | ||
| Haddock · fresh or rawReinke et al. 1975 | Western AtlanticCollection date unreportedbasis not stated | below LOD. | ||
| Hake · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Hake · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Ling, tusk and other cod-like fish · fresh or rawFounder (2018) | Moscow consumer market, RussiaCollection date unreportedbasis not stated | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawBrooke et al. 1981 | PlaiceCollection date unreportedbasis not stated | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawBrooke et al. 1981 | PlaiceCollection date unreportedbasis not stated | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawBrooke et al. 1981 | PlaiceCollection date unreportedbasis not stated | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawBrooke et al. 1981 | PlaiceCollection date unreportedbasis not stated | below LOD. | ||
| Plaice, flounder, sole and turbot · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Halibut · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Halibut · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Halibut · fresh or rawFounder (2018) | Moscow consumer market, RussiaCollection date unreportedbasis not stated | sample value. | ||
| Halibut · fresh or rawKaise et al. 1988 | commercially available, Japan1987basis not stated | not detected. | ||
| Halibut · fresh or rawReinke et al. 1975 | Western AtlanticCollection date unreportedbasis not stated | below LOD. | ||
| Sea bass and barramundi · fresh or rawFounder (2018) | Moscow consumer market, RussiaCollection date unreportedbasis not stated | sample value. | ||
| Sea bream and porgies · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Snapper · fresh or rawFattorini et al. 2004 | Bahia, Cienfuegos Bay, Cuba2001dry weight | mean. | ||
| Snapper · fresh or rawFattorini et al. 2004 | Corona, Cienfuegos Bay, Cuba2001dry weight | mean. | ||
| Croaker and drum · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Croaker and drum · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Croaker and drum · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Emperors and grunts · fresh or rawFattorini et al. 2004 | Bahia, Cienfuegos Bay, Cuba2001dry weight | mean. | ||
| Emperors and grunts · fresh or rawFattorini et al. 2006 | Cienfuegos Bay, CubaCollection date unreporteddry weight | mean. | ||
| Emperors and grunts · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Hairtail and cutlassfish · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Hairtail and cutlassfish · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Hairtail and cutlassfish · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Hairtail and cutlassfish · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | not detected. | ||
| Barracuda · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Sturgeon · fresh or rawBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | not detected. | ||
| Sturgeon · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawNorin et al. 1985 | FuruögrundCollection date unreported | sample value. | ||
| Other marine fish · fresh or rawNorin et al. 1985 | FuruögrundCollection date unreported | sample value. | ||
| Other marine fish · fresh or rawNorin et al. 1985 | SkelleftebuktenCollection date unreported | sample value. | ||
| Other marine fish · fresh or rawNorin et al. 1985 | SkelleftebuktenCollection date unreported | sample value. | ||
| Carp and other cyprinids · fresh or rawNorin et al. 1985 | Lake BodaträskCollection date unreported | sample value. | ||
| Carp and other cyprinids · fresh or rawNorin et al. 1985 | Lake BodaträskCollection date unreported | sample value. | ||
| Carp and other cyprinids · fresh or rawNorin et al. 1985 | Lakes Gäddträsk and SteningsträskCollection date unreported | sample value. | ||
| Carp and other cyprinids · fresh or rawNorin et al. 1985 | Lakes Gäddträsk and SteningsträskCollection date unreported | sample value. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | below LOD. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | below LOD. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | below LOD. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | below LOD. | ||
| Pike · fresh or rawNorin et al. 1985 | Lake BodaträskCollection date unreported | sample value. | ||
| Pike · fresh or rawNorin et al. 1985 | Lake BodaträskCollection date unreported | sample value. | ||
| Pike · fresh or rawNorin et al. 1985 | FuruögrundCollection date unreported | sample value. | ||
| Pike · fresh or rawNorin et al. 1985 | FuruögrundCollection date unreported | sample value. | ||
| Pike · fresh or rawNorin et al. 1985 | Lakes Gäddträsk and SteningsträskCollection date unreported | sample value. | ||
| Pike · fresh or rawNorin et al. 1985 | Lakes Gäddträsk and SteningsträskCollection date unreported | sample value. | ||
| Pike · fresh or rawNorin et al. 1985 | SkelleftebuktenCollection date unreported | sample value. | ||
| Pike · fresh or rawNorin et al. 1985 | SkelleftebuktenCollection date unreported | sample value. | ||
| Perch, walleye and zander · fresh or rawNorin et al. 1985 | Lake BodaträskCollection date unreported | sample value. | ||
| Perch, walleye and zander · fresh or rawNorin et al. 1985 | Lake BodaträskCollection date unreported | sample value. | ||
| Perch, walleye and zander · fresh or rawNorin et al. 1985 | FuruögrundCollection date unreported | sample value. | ||
| Perch, walleye and zander · fresh or rawNorin et al. 1985 | FuruögrundCollection date unreported | sample value. | ||
| Perch, walleye and zander · fresh or rawNorin et al. 1985 | Lakes Gäddträsk and SteningsträskCollection date unreported | sample value. | ||
| Perch, walleye and zander · fresh or rawNorin et al. 1985 | Lakes Gäddträsk and SteningsträskCollection date unreported | sample value. | ||
| Perch, walleye and zander · fresh or rawNorin et al. 1985 | SkelleftebuktenCollection date unreported | sample value. | ||
| Perch, walleye and zander · fresh or rawNorin et al. 1985 | SkelleftebuktenCollection date unreported | sample value. | ||
| Other freshwater fish · fresh or rawNorin et al. 1985 | FuruögrundCollection date unreported | sample value. | ||
| Other freshwater fish · fresh or rawNorin et al. 1985 | FuruögrundCollection date unreported | sample value. | ||
| Other freshwater fish · fresh or rawNorin et al. 1985 | SkelleftebuktenCollection date unreported | sample value. | ||
| Other freshwater fish · fresh or rawNorin et al. 1985 | SkelleftebuktenCollection date unreported | sample value. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2015–2023 | median. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2018–2020dry weight | median. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2017–2021 | median. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region WPRO2020–2022 | median. | ||
| Marine fish, species not stated · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Marine fish, species not stated · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2016–2023 | median. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2020dry weight | median. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region WPRO2020–2024 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2015–2023 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2003–2018 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region WPRO2005–2008 | median. | ||
| Fish, species not stated · fresh or rawEFSA 2009 | EFSA call for data2003–2008basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2009 | EFSA call for data2003–2008basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEFSA et al. 2021 | European countries2013–2018basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEFSA et al. 2021 | European countries2013–2018basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Fish, species not stated · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Fish, species not stated · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Fish, species not stated · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Fish, species not stated · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Fish, species not stated · fresh or rawEuropean 2014 | European countries2003–2012 | mean. | ||
| Fish, species not stated · fresh or rawFood 2016 | UK retail2013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawFood et al. 2014 | UK retail outlets, 2013-20142013–2014basis not stated | below LOD. | ||
11 findings · 3 studies | ||||
| Croaker and drum · smoked, dried, salted or fermentedPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Croaker and drum · smoked, dried, salted or fermentedPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | not detected. | ||
| Hairtail and cutlassfish · smoked, dried, salted or fermentedPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Hairtail and cutlassfish · smoked, dried, salted or fermentedPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | not detected. | ||
| Sturgeon · smoked, dried, salted or fermentedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | not detected. | ||
| Sturgeon · smoked, dried, salted or fermentedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region EURO2015 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region WPRO2002–2024 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region WPRO2022 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region EURO2022 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region EURO2018–2023 | median. | ||
12 findings · 6 studies · 2 spread figures folded in | ||||
| Sturgeon · fish productBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fish productCentre 2012 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 4 µg/kg (range maximum) | ||
| Carp and other cyprinids · fish productCentre 2012 | Hong Kong retail2010–2011basis not stated | range. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2015 | median. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2023 | median. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region WPRO2020 | median. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region WPRO2022 | median. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Fish, species not stated · fish productCentre 2012 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 6–11 µg/kg (range) | ||
| Fish, species not stated · fish productCentre 2012 | Hong Kong retail2010–2011basis not stated | range. | ||
| Fish, species not stated · fish productFood 2011 | Australian state/territory2008 | not detected. | ||
| Fish, species not stated · fish productFood 2011 | Australian state/territory2008 | not detected. | ||
| Fish, species not stated · fish productFood 2019 | Retail/takeaway purchases across2013–2014 | not detected. | ||
2 findings · 2 studies | ||||
| Fish, species not stated · fish sauceMatsumoto-Tanibuchi et… 2019 | local market in JapanCollection date unreported | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand and VietnamCollection date unreportedFish product as reported, mg/L | below LOD. | ||
47 findings · 8 studies | ||||
| Tuna · fresh or rawWHO GEMS/Food | WHO region EURO2016–2017 | median. | ||
| Tuna · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Shark · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region EURO2016 | median. | ||
| Mackerel · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Mackerel · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Horse mackerel, jacks and trevally · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Horse mackerel, jacks and trevally · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region EURO2016–2022 | median. | ||
| Sardine and pilchard · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Sardine and pilchard · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Anchovy · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Shad, hilsa and other herrings · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Salmon · fresh or rawLuvonga et al. 2021 | river-based aquaculture facilityCollection date unreported | mean. | ||
| Salmon · fresh or rawLuvonga et al. 2021 | caught about 15 miles off theCollection date unreported | mean. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region EURO2022–2023 | median. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region EURO2017–2023 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Plaice, flounder, sole and turbot · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Halibut · fresh or rawKaise et al. 1988 | commercially available, Japan1987basis not stated | sample value. | ||
| Sea bream and porgies · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Snapper · fresh or rawFattorini et al. 2004 | Corona, Cienfuegos Bay, Cuba2001dry weight | mean. | ||
| Croaker and drum · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Croaker and drum · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Emperors and grunts · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Hairtail and cutlassfish · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Hairtail and cutlassfish · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Barracuda · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Sturgeon · fresh or rawBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean. | ||
| Other marine fish · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2016–2023 | median. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2021–2023 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2016–2022 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2016–2017 | median. | ||
| Fish, species not stated · fresh or rawEFSA et al. 2024 | EU market2012–2023 | mean. | ||
| Fish, species not stated · fresh or rawEFSA et al. 2024 | EU market2012–2023 | mean. | ||
| Fish, species not stated · fresh or rawEFSA et al. 2024 | EU market2012–2023 | not detected. | ||
| Fish, species not stated · fresh or rawEFSA et al. 2024 | EU market2012–2023 | mean. | ||
| Fish, species not stated · fresh or rawEFSA et al. 2024 | EU market2012–2023 | mean. | ||
| Fish, species not stated · fresh or rawEFSA et al. 2024 | EU market2012–2023 | mean. | ||
| Fish, species not stated · fresh or rawEFSA et al. 2024 | EU market2012–2023 | mean. | ||
4 findings · 2 studies | ||||
| Plaice, flounder, sole and turbot · cookedLiu et al. 2023 | Nanshan Market, Qingdao, ChinaCollection date unreportedbasis not stated | mean. | ||
| Plaice, flounder, sole and turbot · cookedLiu et al. 2023 | Nanshan Market, Qingdao, ChinaCollection date unreportedbasis not stated | mean. | ||
| Sturgeon · cookedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean. | ||
| Sturgeon · cookedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean. | ||
9 findings · 4 studies | ||||
| Croaker and drum · smoked, dried, salted or fermentedPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | not detected. | ||
| Hairtail and cutlassfish · smoked, dried, salted or fermentedPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Sturgeon · smoked, dried, salted or fermentedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean. | ||
| Sturgeon · smoked, dried, salted or fermentedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region EURO2020–2022 | median. | ||
| Fish, species not stated · smoked, dried, salted or fermentedEFSA et al. 2024 | EU market2012–2023 | mean. | ||
| Fish, species not stated · smoked, dried, salted or fermentedEFSA et al. 2024 | EU market2012–2023 | mean. | ||
| Fish, species not stated · smoked, dried, salted or fermentedEFSA et al. 2024 | EU market2012–2023 | mean. | ||
| Fish, species not stated · smoked, dried, salted or fermentedEFSA et al. 2024 | EU market2012–2023 | mean. | ||
2 findings · 2 studies | ||||
| Sturgeon · fish productBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | not detected. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2023 | median. | ||
3 findings · 2 studies | ||||
| Fish, species not stated · cannedWHO GEMS/Food | WHO region EURO2019–2023 | median. | ||
| Fish, species not stated · cannedEFSA et al. 2024 | EU market2012–2023 | mean. | ||
| Fish, species not stated · cannedEFSA et al. 2024 | EU market2012–2023 | mean. | ||
1 finding · 1 study | ||||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand and VietnamCollection date unreportedFish product as reported, mg/L | below LOD. | ||
34 findings · 6 studies | ||||
| Tuna · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Shark · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Mackerel · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Mackerel · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Horse mackerel, jacks and trevally · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Horse mackerel, jacks and trevally · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region EURO2019 | median. | ||
| Sardine and pilchard · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Sardine and pilchard · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Anchovy · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Shad, hilsa and other herrings · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region EURO2022–2023 | median. | ||
| Plaice, flounder, sole and turbot · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Plaice, flounder, sole and turbot · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Halibut · fresh or rawKaise et al. 1988 | commercially available, Japan1987basis not stated | not detected. | ||
| Sea bream and porgies · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Croaker and drum · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Croaker and drum · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Emperors and grunts · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Hairtail and cutlassfish · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Hairtail and cutlassfish · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Barracuda · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Sturgeon · fresh or rawBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | not detected. | ||
| Other marine fish · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2018–2023 | median. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2022 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2016–2022 | median. | ||
| Fish, species not stated · fresh or rawEFSA et al. 2024 | EU market2012–2023 | below LOD. | ||
4 findings · 2 studies | ||||
| Plaice, flounder, sole and turbot · cookedLiu et al. 2023 | Nanshan Market, Qingdao, ChinaCollection date unreportedbasis not stated | below LOD. | ||
| Plaice, flounder, sole and turbot · cookedLiu et al. 2023 | Nanshan Market, Qingdao, ChinaCollection date unreportedbasis not stated | below LOD. | ||
| Sturgeon · cookedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | not detected. | ||
| Sturgeon · cookedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | not detected. | ||
5 findings · 3 studies | ||||
| Croaker and drum · smoked, dried, salted or fermentedPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | not detected. | ||
| Hairtail and cutlassfish · smoked, dried, salted or fermentedPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | not detected. | ||
| Sturgeon · smoked, dried, salted or fermentedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | not detected. | ||
| Sturgeon · smoked, dried, salted or fermentedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | not detected. | ||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region EURO2020 | median. | ||
1 finding · 1 study | ||||
| Sturgeon · fish productBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | not detected. | ||
1 finding · 1 study | ||||
| Fish, species not stated · cannedWHO GEMS/Food | WHO region EURO2019–2020 | median. | ||
1 finding · 1 study | ||||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand and VietnamCollection date unreportedFish product as reported, mg/L | below LOD. | ||
108 findings · 8 studies | ||||
| Tuna · fresh or rawWHO GEMS/Food | WHO region PAHO2018–2020 | median. | ||
| Tuna · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Tuna · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Tuna · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Tuna · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Shark · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Mackerel · fresh or rawWHO GEMS/Food | WHO region PAHO2018–2020 | median. | ||
| Mackerel · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Mackerel · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Mackerel · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Mackerel · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Horse mackerel, jacks and trevally · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Horse mackerel, jacks and trevally · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Horse mackerel, jacks and trevally · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Horse mackerel, jacks and trevally · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Herring · fresh or rawWHO GEMS/Food | WHO region PAHO2018–2020 | median. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region EURO2022 | median. | ||
| Sardine and pilchard · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Sardine and pilchard · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Sardine and pilchard · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Sardine and pilchard · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Sardine and pilchard · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Anchovy · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Anchovy · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Anchovy · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Anchovy · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Shad, hilsa and other herrings · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Shad, hilsa and other herrings · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Shad, hilsa and other herrings · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Shad, hilsa and other herrings · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region PAHO2018–2020 | median. | ||
| Salmon · fresh or rawLuvonga et al. 2021 | river-based aquaculture facilityCollection date unreported | mean. | ||
| Salmon · fresh or rawLuvonga et al. 2021 | caught about 15 miles off theCollection date unreported | mean. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region EURO2022 | median. | ||
| Trout and char · fresh or rawWHO GEMS/Food | WHO region PAHO2020 | median. | ||
| Trout and char · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Trout and char · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region EURO2022 | median. | ||
| Cod · fresh or rawWHO GEMS/Food | WHO region PAHO2020 | median. | ||
| Ling, tusk and other cod-like fish · fresh or rawFounder (2018) | Moscow consumer market, RussiaCollection date unreportedbasis not stated | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Plaice, flounder, sole and turbot · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Plaice, flounder, sole and turbot · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Halibut · fresh or rawFounder (2018) | Moscow consumer market, RussiaCollection date unreportedbasis not stated | sample value. | ||
| Halibut · fresh or rawKaise et al. 1988 | commercially available, Japan1987basis not stated | sample value. | ||
| Halibut · fresh or rawKaise et al. 1988 | commercially available, Japan1987basis not stated | not detected. | ||
| Halibut · fresh or rawKaise et al. 1988 | commercially available, Japan1987basis not stated | not detected. | ||
| Halibut · fresh or rawKaise et al. 1988 | commercially available, Japan1987basis not stated | sample value. | ||
| Sea bass and barramundi · fresh or rawFounder (2018) | Moscow consumer market, RussiaCollection date unreportedbasis not stated | sample value. | ||
| Sea bream and porgies · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Sea bream and porgies · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Sea bream and porgies · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Sea bream and porgies · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Croaker and drum · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Croaker and drum · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Croaker and drum · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Emperors and grunts · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Emperors and grunts · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Emperors and grunts · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Emperors and grunts · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Hairtail and cutlassfish · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Hairtail and cutlassfish · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Hairtail and cutlassfish · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Hairtail and cutlassfish · fresh or rawPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Barracuda · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Barracuda · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Barracuda · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Barracuda · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Sturgeon · fresh or rawBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean. | ||
| Sturgeon · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | not detected. | ||
| Other marine fish · fresh or rawKaise et al. 1988 | Miura Peninsula1987basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Lower Silesia province, PolandCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawTotal Arsenic and… 2019 | Wielkopolska province, PolandCollection date unreporteddry weight | mean. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2022–2023 | median. | ||
| Marine fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2018–2020 | median. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2022–2023 | median. | ||
| Freshwater fish, species not stated · fresh or rawWHO GEMS/Food | WHO region PAHO2020 | median. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region EURO2022 | median. | ||
6 findings · 2 studies | ||||
| Plaice, flounder, sole and turbot · cookedLiu et al. 2023 | Nanshan Market, Qingdao, ChinaCollection date unreportedbasis not stated | mean. | ||
| Plaice, flounder, sole and turbot · cookedLiu et al. 2023 | Nanshan Market, Qingdao, ChinaCollection date unreportedbasis not stated | mean. | ||
| Plaice, flounder, sole and turbot · cookedLiu et al. 2023 | Nanshan Market, Qingdao, ChinaCollection date unreportedbasis not stated | mean. | ||
| Plaice, flounder, sole and turbot · cookedLiu et al. 2023 | Nanshan Market, Qingdao, ChinaCollection date unreportedbasis not stated | mean. | ||
| Sturgeon · cookedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean. | ||
| Sturgeon · cookedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean. | ||
6 findings · 2 studies | ||||
| Croaker and drum · smoked, dried, salted or fermentedPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Croaker and drum · smoked, dried, salted or fermentedPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Hairtail and cutlassfish · smoked, dried, salted or fermentedPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Hairtail and cutlassfish · smoked, dried, salted or fermentedPark et al. 2005 | various markets, KoreaCollection date unreportedbasis not stated | sample value. | ||
| Sturgeon · smoked, dried, salted or fermentedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean. | ||
| Sturgeon · smoked, dried, salted or fermentedBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean. | ||
2 findings · 2 studies | ||||
| Sturgeon · fish productBondareva et al. 2024 | aquaculture farmCollection date unreportedbasis not stated | mean. | ||
| Fish, species not stated · fish productWHO GEMS/Food | WHO region EURO2023 | median. | ||
1 finding · 1 study | ||||
| Fish, species not stated · cannedWHO GEMS/Food | WHO region EURO2022 | median. | ||
24 findings · 1 study | ||||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | mean. | ||
| Fish, species not stated · fish sauceRodriguez et al. 2009 | Thailand or VietnamCollection date unreportedFish product as reported, mg/L | below LOD. | ||
3 findings · 1 study · 1 spread figure folded in | ||||
| Tuna · cannedKosker et al. 2023 | local markets in Türkiye2021 | mean. | ||
| Mackerel · cannedKosker et al. 2023 | local markets in Türkiye2021 | mean. | ||
| Fish, species not stated · cannedKosker et al. 2023 | local markets in Türkiye2021 | mean.Same samples: 10–130 µg/kg (range) | ||
| Fish, species not stated · cannedKosker et al. 2023 | local markets in Türkiye2021 | range. | ||
51 findings · 9 studies · 1 spread figure folded in | ||||
| Tuna · fresh or rawDigoarachchi et al. 2022 | Indian Ocean2015–2017basis not stated | not detected. | ||
| Shark · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Mackerel · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Horse mackerel, jacks and trevally · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Sardine and pilchard · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Salmon · fresh or rawPCBs and Heavy Metals… 2020 | caught at sea off Finnmark2017–2018 | mean. | ||
| Salmon · fresh or rawPCBs and Heavy Metals… 2020 | Lerøy Aurora farm2017–2018 | mean. | ||
| Salmon · fresh or rawPCBs and Heavy Metals… 2020 | Lopphavet, Finnmark, Norway2017–2018 | mean. | ||
| Hake · fresh or rawScientific Research… 2020 | caldera near Sea Diamond wreck2019basis not stated | not detected. | ||
| Ling, tusk and other cod-like fish · fresh or rawScientific Research… 2020 | caldera near Sea Diamond wreck2019basis not stated | not detected. | ||
| Plaice, flounder, sole and turbot · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Sea bream and porgies · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Sea bream and porgies · fresh or rawScientific Research… 2020 | caldera near Sea Diamond wreck2019basis not stated | not detected. | ||
| Snapper · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Croaker and drum · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Croaker and drum · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Emperors and grunts · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Barracuda · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Barracuda · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Scorpionfish and rockfish · fresh or rawScientific Research… 2020 | caldera near Sea Diamond wreck2019basis not stated | not detected. | ||
| Scorpionfish and rockfish · fresh or rawScientific Research… 2020 | caldera near Sea Diamond wreck2019basis not stated | not detected. | ||
| Eel · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Other marine fish · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Other marine fish · fresh or rawEcological and Human… 2023 | five trawl stations2021basis not stated | mean. | ||
| Other marine fish · fresh or rawScientific Research… 2020 | caldera near Sea Diamond wreck2019basis not stated | not detected. | ||
| Other marine fish · fresh or rawScientific Research… 2020 | caldera near Sea Diamond wreck2019basis not stated | not detected. | ||
| Other marine fish · fresh or rawScientific Research… 2020 | caldera near Sea Diamond wreck2019basis not stated | not detected. | ||
| Other marine fish · fresh or rawScientific Research… 2020 | caldera near Sea Diamond wreck2019basis not stated | not detected. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | mean.Same samples: 20–70 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawNajem et al. 2024 | aquacultured in earthen ponds and2022–2023basis not stated | sample value. | ||
| Carp and other cyprinids · fresh or rawOF THE SAFETY OF FISH… 2023 | Private fish farmsCollection date unreportedbasis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawOF THE SAFETY OF FISH… 2023 | Private fish farmsCollection date unreportedbasis not stated | mean. | ||
| Other freshwater fish · fresh or rawHealth Risk Assessment… 2023 | Atrato RiverCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBhoyroo et al. 2015 | EEZ of MauritiusCollection date unreported | range. | ||
| Marine fish, species not stated · fresh or rawBhoyroo et al. 2015 | EEZ of MauritiusCollection date unreported | range. | ||
4 findings · 1 study | ||||
| Herring · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | range. | ||
| Sardine and pilchard · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | range. | ||
| Grey mullet · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | range. | ||
| Grey mullet · smoked, dried, salted or fermentedMorshdy et al. 2023 | Salted fish shops and hypermarketsCollection date unreported | range. | ||
35 findings · 6 studies · 4 spread figures folded in | ||||
| Tuna · cannedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 77–1,050 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 148–989 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 120–667 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Salmon · cannedBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Fish, species not stated · cannedBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Fish, species not stated · cannedDabeka et al. 1995 | Retail, Montreal, Canada1985–1988basis not stated | sample value. | ||
| Fish, species not stated · cannedHan et al. 2024 | Zhejiang Province, China2018–2019basis not stated | mean.Same samples: 2–19,100 µg/kg (range) | ||
| Fish, species not stated · cannedHan et al. 2024 | Zhejiang Province, China2018–2019basis not stated | median. | ||
| Fish, species not stated · cannedHan et al. 2024 | Zhejiang Province, China2018–2019basis not stated | range. | ||
25 findings · 5 studies · 10 spread figures folded in | ||||
| Tuna · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Salmon · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Salmon · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 62 µg/kg (range maximum) | ||
| Salmon · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Cod · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Plaice, flounder, sole and turbot · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 110 µg/kg (range maximum) | ||
| Plaice, flounder, sole and turbot · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Sea bream and porgies · cookedAbbas 2023 | Private fish farm2022dry weight | mean. | ||
| Sea bream and porgies · cookedAbbas 2023 | Private fish farm2022dry weight | mean. | ||
| Sea bream and porgies · cookedAbbas 2023 | Private fish farm2022dry weight | mean. | ||
| Sea bream and porgies · cookedAbbas 2023 | Bardawil Lake, North Sinai, Egypt2022dry weight | mean. | ||
| Sea bream and porgies · cookedAbbas 2023 | Bardawil Lake, North Sinai, Egypt2022dry weight | mean. | ||
| Sea bream and porgies · cookedAbbas 2023 | Bardawil Lake, North Sinai, Egypt2022dry weight | mean. | ||
| Grey mullet · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 61 µg/kg (range maximum) | ||
| Grey mullet · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Grouper · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 27 µg/kg (range maximum) | ||
| Grouper · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Croaker and drum · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 81 µg/kg (range maximum) | ||
| Croaker and drum · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Pomfret · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 63 µg/kg (range maximum) | ||
| Pomfret · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 28–110 µg/kg (range) | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Tilapia · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 23–47 µg/kg (range) | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 73 µg/kg (range maximum) | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other freshwater fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 63 µg/kg (range maximum) | ||
| Other freshwater fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Marine fish, species not stated · cookedDabeka et al. 1995 | Retail, Montreal, Canada1985–1988basis not stated | sample value. | ||
| Freshwater fish, species not stated · cookedDabeka et al. 1995 | Retail, Montreal, Canada1985–1988basis not stated | sample value. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | sample value. | ||
174 findings · 29 studies · 22 spread figures folded in | ||||
| Tuna · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Mackerel · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Mackerel · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Mackerel · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Mackerel · fresh or rawYap et al. 2022 | Setiu2016–2017 | mean. | ||
| King and Spanish mackerel · fresh or rawYap et al. 2022 | Setiu2016–2017 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawYap et al. 2022 | Setiu2016–2017 | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawYap et al. 2022 | Setiu2016–2017dry weight | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawYap et al. 2022 | Setiu2016–2017 | mean. | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | northern sector2018 | mean.Same samples: 110–300 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | northern sector2018 | range. | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | southern sector2018 | mean.Same samples: 110–1,200 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | southern sector2018 | range. | ||
| Anchovy · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Anchovy · fresh or rawSimionov et al. 2023 | Fishing, Black Sea, BulgariaCollection date unreported | mean. | ||
| Shad, hilsa and other herrings · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Shad, hilsa and other herrings · fresh or rawYap et al. 2022 | Setiu2016–2017 | mean. | ||
| Salmon · fresh or rawSimionov et al. 2023 | Aquaculture, NorwayCollection date unreported | mean. | ||
| Trout and char · fresh or rawSimionov et al. 2023 | Aquaculture, RomaniaCollection date unreported | mean. | ||
| Cod · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Hake · fresh or rawSimionov et al. 2023 | Spain; fishing area not specifiedCollection date unreported | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | not detected. | ||
| Plaice, flounder, sole and turbot · fresh or rawTorabi et al. 2024 | Bushehr province ports2022 | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawTorabi et al. 2024 | Bushehr province ports2022basis not stated | range. | ||
| Sea bass and barramundi · fresh or rawBalzani et al. 2026 | Dalyan Lake2021dry weight | mean. | ||
| Sea bream and porgies · fresh or rawAbbas 2023 | Private fish farm2022dry weight | mean. | ||
| Sea bream and porgies · fresh or rawAbbas 2023 | Bardawil Lake, North Sinai, Egypt2022dry weight | mean. | ||
| Sea bream and porgies · fresh or rawBalzani et al. 2026 | Dalyan Lake2021dry weight | mean. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 9–18 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 0.3–3 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | coastal waters of TenerifeCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | Metropolitan zoneCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | North zoneCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | South zoneCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawSimionov et al. 2023 | Aquaculture, GreeceCollection date unreported | mean. | ||
| Red mullet and goatfish · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Red mullet and goatfish · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 2–4 µg/kg (range) | ||
| Red mullet and goatfish · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Grey mullet · fresh or rawBalzani et al. 2026 | Dalyan Lake2021dry weight | mean. | ||
| Grey mullet · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Croaker and drum · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | mean.Same samples: 20–30 µg/kg (range) | ||
| Croaker and drum · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | range. | ||
| Croaker and drum · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Croaker and drum · fresh or rawYap et al. 2022 | Setiu2016–2017 | mean. | ||
| Croaker and drum · fresh or rawYap et al. 2022 | Setiu2016–2017 | mean. | ||
| Pomfret · fresh or rawYap et al. 2022 | Setiu2016–2017 | mean. | ||
| Hairtail and cutlassfish · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | not detected. | ||
| Barracuda · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Barracuda · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Barracuda · fresh or rawTorabi et al. 2024 | Bushehr province ports2022 | mean. | ||
| Barracuda · fresh or rawTorabi et al. 2024 | Bushehr province ports2022basis not stated | range. | ||
| Mahi-mahi · fresh or rawBhoyroo et al. 2015 | EEZ of MauritiusCollection date unreported | mean. | ||
| Scorpionfish and rockfish · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Gurnard · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Other marine fish · fresh or rawHaseeb-ur-Rehman et al. 2023 | harvest area not stated2016–2018 | not detected. | ||
| Other marine fish · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Other marine fish · fresh or rawTorabi et al. 2024 | Bushehr province ports2022 | mean. | ||
| Other marine fish · fresh or rawTorabi et al. 2024 | Bushehr province ports2022basis not stated | range. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R1Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R2Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R3Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R4Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | mean.Same samples: 520–20,000 µg/kg (range) | ||
| Tilapia · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | range. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Lake zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Bukuru unreclaimed mining pits2019basis not stated | mean. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Riyom control point2019basis not stated | sample value. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Bukuru unreclaimed mining pits2019basis not stated | mean. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Riyom control point2019basis not stated | sample value. | ||
| Tilapia · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | min. | ||
| Tilapia · fresh or rawSawe et al. 2023 | Lake Manyara, Tanzania2022dry weight | mean. | ||
| Tilapia · fresh or rawShaalan 2024 | Damietta River Nile2022basis not stated | mean. | ||
| Tilapia · fresh or rawShaalan 2024 | El Rayah El Tawfeeky canal2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Amarat reservoir2022basis not stated | mean.Same samples: 10–150 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Amarat reservoir2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Khawd reservoir2022basis not stated | mean.Same samples: 10–100 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Khawd reservoir2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Surur area2022basis not stated | mean.Same samples: 6–100 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Surur area2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 12021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 22021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 32021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 42021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | mean.Same samples: 5,030 µg/kg (maximum) | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | max. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | range. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Aquaculture, HungaryCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube Delta, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Catfish · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | mean.Same samples: 90–9,200 µg/kg (range) | ||
| Catfish · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | range. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara, Tanzania2022dry weight | mean. | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | mean.Same samples: 630–820 µg/kg (range) | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | range. | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | mean.Same samples: 680–900 µg/kg (range) | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | range. | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | mean.Same samples: 650–780 µg/kg (range) | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | range. | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | mean.Same samples: 640–880 µg/kg (range) | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | range. | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | mean.Same samples: 740–910 µg/kg (range) | ||
| Catfish · fresh or rawSawe et al. 2023 | Lake Manyara2022dry weight | range. | ||
| Catfish · fresh or rawSimionov et al. 2023 | Aquaculture, VietnamCollection date unreported | mean. | ||
| Catfish · fresh or rawSimionov et al. 2023 | Fishing, Danube Delta, RomaniaCollection date unreported | mean. | ||
| Perch, walleye and zander · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | mean. | ||
| Perch, walleye and zander · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Black bass and sunfish · fresh or rawSimionov et al. 2023 | Aquaculture, ItalyCollection date unreported | mean. | ||
| Snakehead · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | mean.Same samples: 330–4,300 µg/kg (range) | ||
| Snakehead · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | range. | ||
| Other freshwater fish · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | left bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Other freshwater fish · fresh or rawNaz et al. 2025 | right bank2021–2022basis not stated | mean. | ||
| Marine fish, species not stated · fresh or rawBhoyroo et al. 2015 | EEZ of MauritiusCollection date unreported | range. | ||
| Marine fish, species not stated · fresh or rawDabeka et al. 1995 | Retail, Montreal, Canada1985–1988basis not stated | sample value. | ||
| Marine fish, species not stated · fresh or rawHan et al. 2024 | Zhejiang Province, China2018–2019basis not stated | mean.Same samples: 1–1,340 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawHan et al. 2024 | Zhejiang Province, China2018–2019basis not stated | median. | ||
| Marine fish, species not stated · fresh or rawHan et al. 2024 | Zhejiang Province, China2018–2019basis not stated | range. | ||
| Marine fish, species not stated · fresh or rawTorabi et al. 2024 | Bushehr province ports2022 | mean. | ||
| Marine fish, species not stated · fresh or rawYap et al. 2022 | Setiu2016–2017dry weight | mean. | ||
| Marine fish, species not stated · fresh or rawYap et al. 2022 | Setiu2016–2017 | mean. | ||
| Marine fish, species not stated · fresh or rawYap et al. 2022 | Setiu2016–2017dry weight | mean.Same samples: 480–3,840 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawYap et al. 2022 | Setiu2016–2017dry weight | median. | ||
| Marine fish, species not stated · fresh or rawYap et al. 2022 | Setiu2016–2017dry weight | range. | ||
| Marine fish, species not stated · fresh or rawYap et al. 2022 | Setiu2016–2017 | mean.Same samples: 110–900 µg/kg (range) | ||
| Marine fish, species not stated · fresh or rawYap et al. 2022 | Setiu2016–2017 | median. | ||
| Marine fish, species not stated · fresh or rawYap et al. 2022 | Setiu2016–2017 | range. | ||
| Freshwater fish, species not stated · fresh or rawDabeka et al. 1995 | Retail, Montreal, Canada1985–1988basis not stated | sample value. | ||
| Freshwater fish, species not stated · fresh or rawHan et al. 2024 | Zhejiang Province, China2018–2019basis not stated | mean.Same samples: 2–10,500 µg/kg (range) | ||
| Freshwater fish, species not stated · fresh or rawHan et al. 2024 | Zhejiang Province, China2018–2019basis not stated | median. | ||
| Freshwater fish, species not stated · fresh or rawHan et al. 2024 | Zhejiang Province, China2018–2019basis not stated | range. | ||
| Fish, species not stated · fresh or rawEFSA 2015 | European countries2003–2012basis not stated | mean. | ||
| Fish, species not stated · fresh or rawEFSA 2015 | European countries2003–2012basis not stated | mean. | ||
| Fish, species not stated · fresh or rawFood 2016 | UK retail2013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawFood et al. 2014 | UK retail outlets, 2013-20142013–2014basis not stated | below LOD. | ||
5 findings · 3 studies · 2 spread figures folded in | ||||
| Carp and other cyprinids · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 39–160 µg/kg (range) | ||
| Carp and other cyprinids · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Fish, species not stated · fish productFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 29–150 µg/kg (range) | ||
| Fish, species not stated · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
6 findings · 1 study · 6 spread figures folded in | ||||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets in Ouagadougou2020basis not stated | median.Same samples: 400–5,650 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets in Ouagadougou2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Bobo Dioulasso2020basis not stated | median.Same samples: 570–5,610 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Bobo Dioulasso2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Cinkasse2020basis not stated | median.Same samples: 3,280–5,650 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Cinkasse2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Dakola2020basis not stated | median.Same samples: 400–5,650 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Dakola2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Niankologo2020basis not stated | median.Same samples: 400–5,610 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Niankologo2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Ouagadougou2020basis not stated | median.Same samples: 400–5,650 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Ouagadougou2020basis not stated | range. | ||
54 findings · 10 studies · 13 spread figures folded in | ||||
| Tuna · cannedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Tuna · cannedKosker et al. 2023 | local markets in Türkiye2021 | mean. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 20–210 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 70–300 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 80–650 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 120–260 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 60–180 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 50–400 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 80–170 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 20–650 µg/kg (range) | ||
| Tuna · cannedRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 370–2,100 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 260–890 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 360–670 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Mackerel · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedEvaluation of… 2025 | SupermarketCollection date unreportedbasis not stated | sample value. | ||
| Sardine and pilchard · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Anchovy · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Salmon · cannedBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Croaker and drum · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Hairtail and cutlassfish · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Carp and other cyprinids · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Fish, species not stated · cannedBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Fish, species not stated · cannedFood 2016 | Major retailers, Dublin, Ireland2012–2014 | range. | ||
| Fish, species not stated · cannedKosker et al. 2023 | local markets in Türkiye2021 | mean.Same samples: 60–4,080 µg/kg (range) | ||
| Fish, species not stated · cannedKosker et al. 2023 | local markets in Türkiye2021 | range. | ||
| Fish, species not stated · cannedSalahel et al. 2025 | randomly selected local markets2022basis not stated | mean.Same samples: 6–9 µg/kg (range) | ||
| Fish, species not stated · cannedSalahel et al. 2025 | randomly selected local markets2022basis not stated | range. | ||
189 findings · 35 studies · 22 spread figures folded in | ||||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 209–5,400 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 95–240 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 34–56 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 65–360 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 80–130 µg/kg (range) | ||
| Tuna · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Tuna · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Swordfish · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 150–180 µg/kg (range) | ||
| Swordfish · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Marlin and other billfish · fresh or rawBhoyroo et al. 2015 | EEZ of MauritiusCollection date unreported | mean. | ||
| Shark · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 160–380 µg/kg (range) | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | mean.Same samples: 70–180 µg/kg (range) | ||
| Shark · fresh or rawRodriguez-Mendivil et al. 2019 | commercial establishments2016 | range. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | below LOD. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Mackerel · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Mackerel · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Mackerel · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Mackerel · fresh or rawKurniawati et al. 2021 | five traditional markets inCollection date unreported | mean. | ||
| Mackerel · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Horse mackerel, jacks and trevally · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | northern sector2018 | mean.Same samples: 120–770 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | northern sector2018 | range. | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | southern sector2018 | mean.Same samples: 110–330 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | southern sector2018 | range. | ||
| Sardine and pilchard · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Anchovy · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Anchovy · fresh or rawSimionov et al. 2023 | Fishing, Black Sea, BulgariaCollection date unreported | mean. | ||
| Shad, hilsa and other herrings · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Shad, hilsa and other herrings · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Salmon · fresh or rawSimionov et al. 2023 | Aquaculture, NorwayCollection date unreported | mean. | ||
| Trout and char · fresh or rawSimionov et al. 2023 | Aquaculture, RomaniaCollection date unreported | mean. | ||
| Cod · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Hake · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Hake · fresh or rawSimionov et al. 2023 | Spain; fishing area not specifiedCollection date unreported | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Plaice, flounder, sole and turbot · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Sea bass and barramundi · fresh or rawBalzani et al. 2026 | Dalyan Lake2021dry weight | mean. | ||
| Sea bass and barramundi · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Sea bass and barramundi · fresh or rawRay et al. 2025 | coastal and inland watersCollection date unreporteddry weight | mean. | ||
| Sea bream and porgies · fresh or rawBalzani et al. 2026 | Dalyan Lake2021dry weight | mean. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 5–40 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 10–30 µg/kg (range) | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Sea bream and porgies · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | coastal waters of TenerifeCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | Metropolitan zoneCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | North zoneCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | South zoneCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station I2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station II2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Sea bream and porgies · fresh or rawSimionov et al. 2023 | Aquaculture, GreeceCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | not detected. | ||
| Sea bream and porgies · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | not detected. | ||
| Red mullet and goatfish · fresh or rawCopat et al. 2013 | Gulf of Catania2012 | mean. | ||
| Red mullet and goatfish · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | mean.Same samples: 20–30 µg/kg (range) | ||
| Red mullet and goatfish · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | range. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Aliaga Bay2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station I2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station II2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Red mullet and goatfish · fresh or rawPazi et al. 2017 | Izmir Bay station III2009–2014 | mean. | ||
| Grey mullet · fresh or rawBalzani et al. 2026 | Dalyan Lake2021dry weight | mean. | ||
| Grey mullet · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Grey mullet · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Grey mullet · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Snapper · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Croaker and drum · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Croaker and drum · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Croaker and drum · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | not detected. | ||
| Pomfret · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Pomfret · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Hairtail and cutlassfish · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Barracuda · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Barracuda · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Mahi-mahi · fresh or rawBhoyroo et al. 2015 | EEZ of MauritiusCollection date unreported | mean. | ||
| Scorpionfish and rockfish · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Scorpionfish and rockfish · fresh or rawOlgunoglu et al. 2025 | Izmir Bay, Türkiye2023–2024 | mean. | ||
| Gurnard · fresh or rawDi et al. 2020 | Augusta–Melilli–Priolo area2018 | sample value. | ||
| Other marine fish · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Other marine fish · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Other marine fish · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Other marine fish · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | mean. | ||
| Other marine fish · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Other marine fish · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawJob et al. 2023 | Thondi coastCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 55–218 µg/kg (range) | ||
| Other marine fish · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Other marine fish · fresh or rawRay et al. 2025 | coastal and inland watersCollection date unreporteddry weight | mean. | ||
| Other marine fish · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | not detected. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R1Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R2Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R3Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawGupta et al. 2024 | Cauvery River site R4Collection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | mean.Same samples: 540–2,700 µg/kg (range) | ||
| Tilapia · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | range. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Lake zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawRay et al. 2025 | coastal and inland watersCollection date unreporteddry weight | mean. | ||
| Tilapia · fresh or rawShaalan 2024 | Damietta River Nile2022basis not stated | mean. | ||
| Tilapia · fresh or rawShaalan 2024 | El Rayah El Tawfeeky canal2022basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Amarat reservoir2022basis not stated | mean.Same samples: 10–70 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Amarat reservoir2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Khawd reservoir2022basis not stated | mean.Same samples: 10–90 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Al Khawd reservoir2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Surur area2022basis not stated | mean.Same samples: 10–30 µg/kg (range) | ||
| Carp and other cyprinids · fresh or rawAl et al. 2024 | Surur area2022basis not stated | range. | ||
| Carp and other cyprinids · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 12021–2022 | below LOD. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 22021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 32021–2022 | mean.Same samples: 160 µg/kg (maximum) | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 32021–2022 | max. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Bečva site 42021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | mean. | ||
| Carp and other cyprinids · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | below LOD. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawLiang et al. 2019 | Beijing, ChinaCollection date unreporteddry weight | mean. | ||
| Carp and other cyprinids · fresh or rawRajeshkumar et al. 2018 | Meiliang Bay2016 | mean. | ||
| Carp and other cyprinids · fresh or rawRajeshkumar et al. 2018 | Meiliang Bay2016 | mean. | ||
| Carp and other cyprinids · fresh or rawRajeshkumar et al. 2018 | Meiliang Bay2016 | mean. | ||
| Carp and other cyprinids · fresh or rawRajeshkumar et al. 2018 | Meiliang Bay2016 | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Aquaculture, HungaryCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube Delta, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Catfish · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Catfish · fresh or rawBioaccumulation and… 2019 | River Ganga basin2016basis not stated | mean. | ||
| Catfish · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | mean.Same samples: 2,000–3,300 µg/kg (range) | ||
| Catfish · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | range. | ||
| Catfish · fresh or rawSimionov et al. 2023 | Aquaculture, VietnamCollection date unreported | mean. | ||
| Catfish · fresh or rawSimionov et al. 2023 | Fishing, Danube Delta, RomaniaCollection date unreported | mean. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Badagry Creek2011–2013basis not stated | range. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Badagry Creek2011–2013basis not stated | mean. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Badagry Creek2011–2013basis not stated | mean. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Lower zone, Badagry Creek, Nigeria2011–2013basis not stated | mean. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Middle zone2011–2013basis not stated | mean. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Upper zone, Badagry Creek, Nigeria2011–2013basis not stated | mean. | ||
| Catfish · fresh or rawVariability in Levels… 2015 | Badagry Creek2011–2013basis not stated | mean. | ||
| Perch, walleye and zander · fresh or rawContent of heavy metals… 2025 | River Svratka2021–2022 | below LOD. | ||
| Perch, walleye and zander · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Black bass and sunfish · fresh or rawSimionov et al. 2023 | Aquaculture, ItalyCollection date unreported | mean. | ||
| Snakehead · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | mean.Same samples: 1,100–2,300 µg/kg (range) | ||
| Snakehead · fresh or rawIslam et al. 2015 | Korotoa River and/or markets2012 | range. | ||
| Other freshwater fish · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | mean. | ||
| Marine fish, species not stated · fresh or rawBaki et al. 2018 | Saint Martin's IslandCollection date unreported | below LOD. | ||
| Marine fish, species not stated · fresh or rawBhoyroo et al. 2015 | EEZ of MauritiusCollection date unreported | range. | ||
| Marine fish, species not stated · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | range. | ||
| Marine fish, species not stated · fresh or rawBioaccumulation of… 2019 | Karnaphuli River estuary2018dry weight | mean. | ||
| Marine fish, species not stated · fresh or rawZhao et al. 2016 | traditional seafood markets andCollection date unreported | range. | ||
| Fish, species not stated · fresh or rawFood 2016 | UK retail2013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawFood et al. 2014 | UK retail outlets, 2013-20142013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawFood et al. 2014 | UK retail outlets, 2013-20142013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawLoutfy et al. 2012 | 'All the samples were produced2007 | mean.Same samples: 12.6–26.1 µg/kg (range) | ||
| Fish, species not stated · fresh or rawLoutfy et al. 2012 | 'All the samples were produced2007 | range. | ||
5 findings · 2 studies | ||||
| Salmon · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Cod · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Tilapia · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | sample value. | ||
8 findings · 3 studies · 3 spread figures folded in | ||||
| Cod · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean.Same samples: 30–80 µg/kg (range) | ||
| Cod · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | range. | ||
| Tilapia · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean.Same samples: 10–140 µg/kg (range) | ||
| Tilapia · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | range. | ||
| Catfish · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean.Same samples: 40–80 µg/kg (range) | ||
| Catfish · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | range. | ||
| Fish, species not stated · fish productFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | mean. | ||
| Fish, species not stated · fish productCammilleri et al. 2025 | Italy-based purchase on e-commerce2022–2023 | range. | ||
6 findings · 1 study · 6 spread figures folded in | ||||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets in Ouagadougou2020basis not stated | median.Same samples: 230–3,090 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets in Ouagadougou2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Bobo Dioulasso2020basis not stated | median.Same samples: 890–2,670 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Bobo Dioulasso2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Cinkasse2020basis not stated | median.Same samples: 890–2,090 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Cinkasse2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Dakola2020basis not stated | median.Same samples: 230–3,090 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Dakola2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Niankologo2020basis not stated | median.Same samples: 890–2,670 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Niankologo2020basis not stated | range. | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Ouagadougou2020basis not stated | median.Same samples: 230–3,090 µg/kg (range) | ||
| Fish, species not stated · smoked, dried, salted or fermentedBazie et al. 2022 | open markets, Ouagadougou2020basis not stated | range. | ||
6 findings · 1 study | ||||
| Shark · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Horse mackerel, jacks and trevally · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Sardine and pilchard · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Plaice, flounder, sole and turbot · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Croaker and drum · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
| Other marine fish · fresh or rawChemical Speciation of… 2023 | open markets and supermarketsCollection date unreportedbasis not stated | below LOD. | ||
38 findings · 6 studies · 4 spread figures folded in | ||||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Tuna · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Tuna · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 10,800–33,900 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 9,570–33,100 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 9,310–19,700 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Mackerel · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Herring · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | below LOD. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedDe et al. 2021 | popular supermarketsCollection date unreported | mean. | ||
| Sardine and pilchard · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Salmon · cannedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Salmon · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Fish, species not stated · cannedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cannedFood 2016 | Major retailers, Dublin, Ireland2012–2014 | range. | ||
| Fish, species not stated · cannedKosker et al. 2023 | local markets in Türkiye2021 | mean.Same samples: 1,410–14,500 µg/kg (range) | ||
| Fish, species not stated · cannedKosker et al. 2023 | local markets in Türkiye2021 | range. | ||
81 findings · 6 studies · 4 spread figures folded in | ||||
| Tuna · cookedWHO GEMS/Food | WHO region EURO2007–2008 | median. | ||
| Tuna · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | not detected. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreported | not detected. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | not detected. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreported | not detected. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | not detected. | ||
| Mackerel · cookedDordevic et al. 2019 | NorwayCollection date unreported | not detected. | ||
| Salmon · cookedWHO GEMS/Food | WHO region EURO2007–2009 | median. | ||
| Salmon · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreported | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreported | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreported | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreported | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreported | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreported | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreported | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | mean. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreported | mean. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreporteddry weight | not detected. | ||
| Salmon · cookedDordevic et al. 2019 | NorwayCollection date unreported | not detected. | ||
| Cod · cookedWang et al. 2020 | Jilin Province, China2015–2016basis not stated | mean. | ||
| Cod · cookedWang et al. 2020 | other areas of Jilin Province2015–2016basis not stated | mean. | ||
| Cod · cookedWang et al. 2020 | Songhua River Basin area2015–2016basis not stated | mean. | ||
| Plaice, flounder, sole and turbot · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Grey mullet · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 530–1,100 µg/kg (range) | ||
| Grey mullet · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Grouper · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Croaker and drum · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Pomfret · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 220 µg/kg (range maximum) | ||
| Pomfret · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 140–280 µg/kg (range) | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 410 µg/kg (range maximum) | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Carp and other cyprinids · cookedWang et al. 2020 | Jilin Province, China2015–2016basis not stated | mean. | ||
| Carp and other cyprinids · cookedWang et al. 2020 | other areas of Jilin Province2015–2016basis not stated | mean. | ||
| Carp and other cyprinids · cookedWang et al. 2020 | Songhua River Basin area2015–2016basis not stated | mean. | ||
| Other freshwater fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region EURO2007–2009 | median. | ||
| Fish, species not stated · cookedANSES 2026 | France retail2021–2022 | mean. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cookedWang et al. 2020 | Jilin Province, China2015–2016basis not stated | mean. | ||
61 findings · 11 studies · 7 spread figures folded in | ||||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 6,270–44,200 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 6,010–14,000 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 4,160–5,040 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 283–959 µg/kg (range) | ||
| Tuna · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tuna · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Mackerel · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Mackerel · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | northern sector2018 | mean.Same samples: 110–21,000 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | northern sector2018 | range. | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | southern sector2018 | mean.Same samples: 110–17,000 µg/kg (range) | ||
| Sardine and pilchard · fresh or rawBauer et al. 2023 | southern sector2018 | range. | ||
| Anchovy · fresh or rawSimionov et al. 2023 | Fishing, Black Sea, BulgariaCollection date unreported | mean. | ||
| Shad, hilsa and other herrings · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Salmon · fresh or rawSimionov et al. 2023 | Aquaculture, NorwayCollection date unreported | mean. | ||
| Trout and char · fresh or rawSimionov et al. 2023 | Aquaculture, RomaniaCollection date unreported | mean. | ||
| Cod · fresh or rawSimionov et al. 2023 | FishingCollection date unreported | mean. | ||
| Hake · fresh or rawSimionov et al. 2023 | Spain; fishing area not specifiedCollection date unreported | mean. | ||
| Sea bass and barramundi · fresh or rawLevent 2022 | Sinop fish markets, Turkey2020 | range. | ||
| Sea bass and barramundi · fresh or rawLevent 2022 | Sinop fish markets, Turkey2020 | mean. | ||
| Sea bass and barramundi · fresh or rawLevent 2022 | Sinop fish markets, Turkey2020 | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | coastal waters of TenerifeCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | Metropolitan zoneCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | North zoneCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawGutierrez-Ravelo et al. 2020 | South zoneCollection date unreported | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Sea bream and porgies · fresh or rawSimionov et al. 2023 | Aquaculture, GreeceCollection date unreported | mean. | ||
| Grey mullet · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Grey mullet · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Grouper · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Grouper · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Croaker and drum · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Emperors and grunts · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Barracuda · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Scorpionfish and rockfish · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Other marine fish · fresh or rawHuman health… 2026 | Turkish Northeastern Mediterranean2025 | mean. | ||
| Other marine fish · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | mean.Same samples: 326–949 µg/kg (range) | ||
| Other marine fish · fresh or rawLozano-Bilbao et al. 2023 | Canary Islands waters2021 | range. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Lake zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | range. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawKovacik et al. 2024 | university experimental pondCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Aquaculture, HungaryCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube Delta, RomaniaCollection date unreported | mean. | ||
| Carp and other cyprinids · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Catfish · fresh or rawSimionov et al. 2023 | Aquaculture, VietnamCollection date unreported | mean. | ||
| Catfish · fresh or rawSimionov et al. 2023 | Fishing, Danube Delta, RomaniaCollection date unreported | mean. | ||
| Perch, walleye and zander · fresh or rawSimionov et al. 2023 | Fishing, Danube River, RomaniaCollection date unreported | mean. | ||
| Black bass and sunfish · fresh or rawSimionov et al. 2023 | Aquaculture, ItalyCollection date unreported | mean. | ||
| Other freshwater fish · fresh or rawMohamed et al. 2023 | El-Obour city fish market, Egypt2022 | mean. | ||
| Fish, species not stated · fresh or rawFood 2016 | UK retail2013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawFood et al. 2014 | UK retail outlets, 2013-20142013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawFood et al. 2014 | UK retail outlets, 2013-20142013–2014basis not stated | mean. | ||
5 findings · 3 studies · 2 spread figures folded in | ||||
| Carp and other cyprinids · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 690–2,500 µg/kg (range) | ||
| Carp and other cyprinids · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Fish, species not stated · fish productANSES 2026 | France retail2021–2022 | mean. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 2,700–5,200 µg/kg (range) | ||
| Fish, species not stated · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
3 findings · 1 study | ||||
| Fish, species not stated · fish sauceAbdullah 2009 | Fish sauce sample ACollection date unreportedbasis not stated | sample value. | ||
| Fish, species not stated · fish sauceAbdullah 2009 | Fish sauce sample BCollection date unreportedbasis not stated | sample value. | ||
| Fish, species not stated · fish sauceAbdullah 2009 | Fish sauce sample CCollection date unreportedbasis not stated | sample value. | ||
45 findings · 11 studies · 4 spread figures folded in | ||||
| Tuna · cannedBartels et al. 2023 | Cape Coast marketCollection date unreportedbasis not stated | mean. | ||
| Tuna · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Tuna · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | not detected. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | not detected. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | not detected. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | not detected. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | not detected. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | not detected. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | not detected. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | not detected. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | not detected. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | not detected. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | not detected. | ||
| Tuna · cannedLima et al. 2017 | largest markets in the Campinas2015basis not stated | not detected. | ||
| Tuna · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Tuna · cannedOlmedo et al. 2013 | Andalusia, Spain2009–2010 | median. | ||
| Tuna · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 38,200–116,000 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 34,000–44,800 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | mean.Same samples: 32,600–43,100 µg/kg (range) | ||
| Tuna · cannedRüstemli et al. 2026 | large retail chains2022 | range. | ||
| Tuna · cannedTrandafir et al. 2012 | local marketsCollection date unreportedbasis not stated | mean. | ||
| Tuna · cannedTrandafir et al. 2012 | local marketsCollection date unreportedbasis not stated | mean. | ||
| Mackerel · cannedBartels et al. 2023 | Cape Coast marketCollection date unreportedbasis not stated | mean. | ||
| Mackerel · cannedChristine et al. 1971 | Minced mackerelCollection date unreportedbasis not stated | sample value. | ||
| Mackerel · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Mackerel · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Mackerel · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Herring · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Sardine and pilchard · cannedBartels et al. 2023 | Cape Coast marketCollection date unreportedbasis not stated | mean. | ||
| Sardine and pilchard · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Sardine and pilchard · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Sardine and pilchard · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Sardine and pilchard · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Anchovy · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Anchovy · cannedOlmedo et al. 2013 | Spain2009–2010 | median. | ||
| Salmon · cannedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Salmon · cannedHussein et al. 2024 | retail shops / fish market2023 | mean. | ||
| Croaker and drum · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Hairtail and cutlassfish · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Carp and other cyprinids · cannedGu et al. 2014 | retail outlets2011 | mean. | ||
| Fish, species not stated · cannedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cannedFood 2016 | Major retailers, Dublin, Ireland2012–2014 | range. | ||
| Fish, species not stated · cannedYe et al. 2026 | provincial origin of cans in Table2018–2019dry weight | mean.Same samples: up to 1,510 µg/kg (range maximum) | ||
| Fish, species not stated · cannedYe et al. 2026 | provincial origin of cans in Table2018–2019dry weight | median. | ||
| Fish, species not stated · cannedYe et al. 2026 | provincial origin of cans in Table2018–2019dry weight | range. | ||
22 findings · 3 studies · 6 spread figures folded in | ||||
| Tuna · cookedWHO GEMS/Food | WHO region EURO2007–2008 | median. | ||
| Tuna · cookedWHO GEMS/Food | WHO region WPRO2010–2011 | median. | ||
| Tuna · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 57 µg/kg (range maximum) | ||
| Tuna · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Salmon · cookedWHO GEMS/Food | WHO region EURO2007–2009 | median. | ||
| Salmon · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Plaice, flounder, sole and turbot · cookedWHO GEMS/Food | WHO region WPRO2010–2011 | median. | ||
| Plaice, flounder, sole and turbot · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Grey mullet · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Grouper · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 110 µg/kg (range maximum) | ||
| Grouper · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Croaker and drum · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 17–130 µg/kg (range) | ||
| Croaker and drum · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Pomfret · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 13–82 µg/kg (range) | ||
| Pomfret · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 25–33 µg/kg (range) | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 16–30 µg/kg (range) | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Carp and other cyprinids · cookedWHO GEMS/Food | WHO region WPRO2010–2011 | median. | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Other freshwater fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Bream (species group not stated) · cookedWHO GEMS/Food | WHO region WPRO2010 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region EURO2007–2009 | median. | ||
| Fish, species not stated · cookedWHO GEMS/Food | WHO region WPRO1998–2011 | median. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | below LOD. | ||
23 findings · 6 studies · 1 spread figure folded in | ||||
| Tuna · fresh or rawWHO GEMS/Food | WHO region WPRO2000 | median. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | below LOD. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | below LOD. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | below LOD. | ||
| Sardine and pilchard · fresh or rawWHO GEMS/Food | WHO region WPRO2000–2002 | median. | ||
| Salmon · fresh or rawWHO GEMS/Food | WHO region WPRO1998–2005 | median. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Lake zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | North zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | South zone2018–2019dry weight | mean. | ||
| Tilapia · fresh or rawMarriott et al. 2023 | Strait zone2018–2019dry weight | mean. | ||
| Fish, species not stated · fresh or rawWHO GEMS/Food | WHO region WPRO1998–2005 | median. | ||
| Fish, species not stated · fresh or rawFood 2016 | UK retail2013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawFood et al. 2014 | UK retail outlets, 2013-20142013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawFood et al. 2014 | UK retail outlets, 2013-20142013–2014basis not stated | mean. | ||
| Fish, species not stated · fresh or rawYe et al. 2026 | Zhejiang Province supply2018–2019dry weight | mean.Same samples: up to 10,300 µg/kg (range maximum) | ||
| Fish, species not stated · fresh or rawYe et al. 2026 | Zhejiang Province supply2018–2019dry weight | median. | ||
| Fish, species not stated · fresh or rawYe et al. 2026 | Zhejiang Province supply2018–2019dry weight | range. | ||
4 findings · 2 studies · 1 spread figure folded in | ||||
| Carp and other cyprinids · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 16–44 µg/kg (range) | ||
| Fish, species not stated · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
1 finding · 1 study | ||||
| Fish, species not stated · smoked, dried, salted or fermentedWHO GEMS/Food | WHO region WPRO2001–2002 | median. | ||
1 finding · 1 study | ||||
| Tuna · cannedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
3 findings · 1 study | ||||
| Salmon · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Cod · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
| Tilapia · cookedFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
4 findings · 1 study | ||||
| Tilapia · fresh or rawOkonofua et al. 2024 | Bukuru unreclaimed mining pits2019basis not stated | not detected. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Riyom control point2019basis not stated | not detected. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Bukuru unreclaimed mining pits2019basis not stated | not detected. | ||
| Tilapia · fresh or rawOkonofua et al. 2024 | Riyom control point2019basis not stated | not detected. | ||
1 finding · 1 study | ||||
| Fish, species not stated · fish productFDA TDS FY2018–FY2020 | United StatesCollection date unreported | median. | ||
14 findings · 2 studies · 5 spread figures folded in | ||||
| Tuna · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 1 µg/kg (range maximum) | ||
| Tuna · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Salmon · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Plaice, flounder, sole and turbot · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 6 µg/kg (range maximum) | ||
| Plaice, flounder, sole and turbot · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Grey mullet · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Grouper · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Croaker and drum · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Pomfret · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 3 µg/kg (range maximum) | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 1 µg/kg (range maximum) | ||
| Other marine fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 2 µg/kg (range maximum) | ||
| Carp and other cyprinids · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Other freshwater fish · cookedCentre 2013 | Hong Kong retail2010–2011basis not stated | not detected. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | below LOD. | ||
| Fish, species not stated · cookedBaxter et al. 2015 | UK retail2014 | sample value. | ||
21 findings · 4 studies | ||||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | below LOD. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | below LOD. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | mean. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught in the sea area between2017 | below LOD. | ||
| Shark · fresh or rawSang et al. 2019 | by-caught by drift gillnets in the2017 | below LOD. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Carp and other cyprinids · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | Valdeazogues River transectCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | Castilseras reservoirCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | El Entredicho open pit lakeCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | La Colada reservoirCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PLPCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PPACollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PPMCollection date unreporteddry weight | mean. | ||
| Black bass and sunfish · fresh or rawBarquero et al. 2024 | tabla PTHCollection date unreporteddry weight | mean. | ||
| Other freshwater fish · fresh or rawIn et al. 2016 | Buriganga River, Bangladesh2013 | mean. | ||
| Fish, species not stated · fresh or rawFood et al. 2014 | UK retail outlets, 2013-20142013–2014basis not stated | below LOD. | ||
2 findings · 1 study | ||||
| Salmon · cannedBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · cannedBaxter et al. 2015 | UK retail2014 | sample value. | ||
4 findings · 2 studies · 2 spread figures folded in | ||||
| Carp and other cyprinids · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: up to 1 µg/kg (range maximum) | ||
| Carp and other cyprinids · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productBaxter et al. 2015 | UK retail2014 | sample value. | ||
| Fish, species not stated · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | mean.Same samples: 2–6 µg/kg (range) | ||
| Fish, species not stated · fish productCentre 2013 | Hong Kong retail2010–2011basis not stated | range. | ||
Shared dataset methods and interpretation
Source summaries retain their original statistic, material, basis and censoring. Each source drawer identifies methods and overlapping samples. No matched reference or pooled distribution is inferred.
HMI Tuna (canned) tHg reference · 4 sampling families
Reference and scope
HMI Tuna (canned) tHg reference · 4 sampling families. Fish, wet weight; Tuna, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 221 | 631 | 1170 |
| Alternative weighting | 221 | 631 | 1170 |
10 reference units; 4 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 25% |
| Rodriguez-Mendivil et al. 2019 | 2 | 25% |
| Rüstemli et al. 2026 | 6 | 25% |
| Olmedo et al. 2013 | 1 | 25% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-tuna-canned-fish-wet-weight:76bbf3b79c3f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (canned) tHg reference · 3 sampling families
Reference and scope
HMI Tuna (canned) tHg reference · 3 sampling families. Fish, basis not stated; Tuna, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 58.8 | 250 |
| Alternative weighting | 30 | 58.8 | 250 |
3 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 33% |
| Blanco et al. 2023 | 1 | 33% |
| Pawlaczyk et al. 2020 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-tuna-canned-fish-basis-not-stated:414d910078b1
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fish product) tHg reference · 1 sampling family
Reference and scope
HMI Tuna (fish product) tHg reference · 1 sampling family. Fish, basis not stated; Tuna, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 30 | 30 |
| Alternative weighting | 30 | 30 | 30 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-tuna-fish-product-fish-basis-not-stated:7530d04ed383
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fish product) tHg reference · 1 sampling family
Reference and scope
HMI Tuna (fish product) tHg reference · 1 sampling family. Fish, dry weight; Tuna, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 13.5 | 326 | 638 |
| Alternative weighting | 13.5 | 326 | 638 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Maria et al. 2022 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-tuna-fish-product-fish-dry-weight:1e9a598aa335
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) tHg reference · 6 sampling families
Reference and scope
HMI Tuna (fresh or raw) tHg reference · 6 sampling families. Fish, wet weight; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 139 | 234 | 470 |
| Alternative weighting | 139 | 234 | 470 |
144 reference units; 6 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 15 | 17% |
| Total mercury… 1982 | 120 | 17% |
| EFSA 2012 | 3 | 17% |
| Garofalo et al. 2025 | 1 | 17% |
| Olmedo et al. 2013 | 1 | 17% |
| Seafood 2022 | 4 | 17% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-tuna-fresh-fish-wet-weight:93d94b06f257
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) tHg reference · 5 sampling families
Reference and scope
HMI Tuna (fresh or raw) tHg reference · 5 sampling families. Fish, basis not stated; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 160 | 290 | 620 |
| Alternative weighting | 160 | 290 | 620 |
27 reference units; 5 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Brodziak-Dopierala et al. 2023 | 2 | 20% |
| European et al. 2004 | 3 | 20% |
| Lin et al. 2021 | 3 | 20% |
| Watanabe et al. 2017 | 6 | 20% |
| Yamashita 2024 | 13 | 20% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-tuna-fresh-fish-basis-not-stated:900251854ede
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Tuna (fresh or raw) tHg reference · 1 sampling family. Fish, dry weight; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 263 | 316 | 350 |
| Alternative weighting | 263 | 316 | 350 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Seafood 2022 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-tuna-fresh-fish-dry-weight:cc914f278e9d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (smoked, dried, salted or fermented) tHg reference · 1 sampling family
Reference and scope
HMI Tuna (smoked, dried, salted or fermented) tHg reference · 1 sampling family. Fish, basis not stated; Tuna, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 30 | 30 |
| Alternative weighting | 30 | 30 | 30 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-tuna-smoked-dried-salted-fermented-fish-basis-not-stated:46d7b59d6c80
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Bonito (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Bonito (fresh or raw) tHg reference · 2 sampling families. Fish, wet weight; Bonito, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 125 | 263 | 400 |
| Alternative weighting | 125 | 263 | 400 |
4 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 50% |
| Seafood 2022 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-bonito-fresh-fish-wet-weight:cb57ccbe6282
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Bonito (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Bonito (fresh or raw) tHg reference · 1 sampling family. Fish, dry weight; Bonito, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 543 | 543 | 543 |
| Alternative weighting | 543 | 543 | 543 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Seafood 2022 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-bonito-fresh-fish-dry-weight:7ce13b803103
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Swordfish (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Swordfish (fresh or raw) tHg reference · 3 sampling families. Fish, basis not stated; Swordfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 760 | 910 | 1570 |
| Alternative weighting | 760 | 910 | 1570 |
6 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Yamashita 2024 | 1 | 33% |
| Blanco et al. 2023 | 4 | 33% |
| Watanabe et al. 2017 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-swordfish-fresh-fish-basis-not-stated:229cf9fe40d4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Swordfish (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Swordfish (fresh or raw) tHg reference · 3 sampling families. Fish, wet weight; Swordfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 540 | 630 | 1010 |
| Alternative weighting | 540 | 630 | 1010 |
5 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 33% |
| Garofalo et al. 2025 | 1 | 33% |
| Olmedo et al. 2013 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-swordfish-fresh-fish-wet-weight:325e528d75ca
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marlin and other billfish (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Marlin and other billfish (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; Marlin and other billfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 30 | 30 |
| Alternative weighting | 30 | 30 | 30 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Lin et al. 2021 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-marlin-billfish-fresh-fish-basis-not-stated:4ee4ac52ca6d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shark (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Shark (fresh or raw) tHg reference · 2 sampling families. Fish, basis not stated; Shark, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 165 | 510 | 17400 |
| Alternative weighting | 165 | 510 | 17400 |
5 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Global Patterns of… 2026 | 3 | 50% |
| Lin et al. 2021 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-shark-fresh-fish-basis-not-stated:0fc313020f5a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shark (fresh or raw) tHg reference · 6 sampling families
Reference and scope
HMI Shark (fresh or raw) tHg reference · 6 sampling families. Fish, wet weight; Shark, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 153 | 495 | 698 |
| Alternative weighting | 153 | 495 | 698 |
33 reference units; 6 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Christian et al. 2024 | 1 | 17% |
| Sang et al. 2019 | 25 | 17% |
| EFSA 2012 | 3 | 17% |
| Garofalo et al. 2025 | 1 | 17% |
| Harding et al. 2018 | 1 | 17% |
| Olmedo et al. 2013 | 2 | 17% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
- Christian et al. 2024
- Sang et al. 2019
- EFSA 2012
- Garofalo et al. 2025
- Harding et al. 2018
- Olmedo et al. 2013
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-shark-fresh-fish-wet-weight:cc36c710c2fb
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Ray and skate (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Ray and skate (fresh or raw) tHg reference · 2 sampling families. Fish, wet weight; Ray and skate, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 88.5 | 108 | 108 |
| Alternative weighting | 88.5 | 108 | 108 |
7 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 50% |
| Seafood 2022 | 4 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-ray-skate-fresh-fish-wet-weight:e7d290905834
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Ray and skate (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Ray and skate (fresh or raw) tHg reference · 1 sampling family. Fish, dry weight; Ray and skate, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 405 | 459 | 520 |
| Alternative weighting | 405 | 459 | 520 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Seafood 2022 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-ray-skate-fresh-fish-dry-weight:a90e4cc544d3
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (canned) tHg reference · 2 sampling families
Reference and scope
HMI Mackerel (canned) tHg reference · 2 sampling families. Fish, wet weight; Mackerel, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 322 | 624 |
| Alternative weighting | 20 | 322 | 624 |
2 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Djedjibegovic et al. 2020 | 1 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-mackerel-canned-fish-wet-weight:ce72168ff58c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (canned) tHg reference · 1 sampling family
Reference and scope
HMI Mackerel (canned) tHg reference · 1 sampling family. Fish, basis not stated; Mackerel, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 40 | 40 | 40 |
| Alternative weighting | 40 | 40 | 40 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-mackerel-canned-fish-basis-not-stated:13e260591d8b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) tHg reference · 5 sampling families
Reference and scope
HMI Mackerel (fresh or raw) tHg reference · 5 sampling families. Fish, wet weight; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 22 | 40 | 48.4–50.9 (bounded) |
| Alternative weighting | 22 | 40 | 48.4–50.9 (bounded) |
25 reference units; 5 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 16 | 20% |
| EFSA 2012 | 3 | 20% |
| Harding et al. 2018 | 1 | 20% |
| Olmedo et al. 2013 | 1 | 20% |
| Seafood 2022 | 4 | 20% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-mackerel-fresh-fish-wet-weight:a6ef75ae4b38
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Mackerel (fresh or raw) tHg reference · 3 sampling families. Fish, basis not stated; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 58 | 170 |
| Alternative weighting | 30 | 58 | 170 |
5 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Brodziak-Dopierala et al. 2023 | 1 | 33% |
| European et al. 2004 | 3 | 33% |
| Watanabe et al. 2017 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-mackerel-fresh-fish-basis-not-stated:313de0bfb05c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Mackerel (fresh or raw) tHg reference · 1 sampling family. Fish, dry weight; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 221 | 265 | 313 |
| Alternative weighting | 221 | 265 | 313 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Seafood 2022 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-mackerel-fresh-fish-dry-weight:7e5f744c1b01
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI King and Spanish mackerel (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI King and Spanish mackerel (fresh or raw) tHg reference · 1 sampling family. Fish, dry weight; King and Spanish mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 262 | 315 | 368 |
| Alternative weighting | 262 | 315 | 368 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Seafood 2022 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-king-spanish-mackerel-fresh-fish-dry-weight:7f73be749f27
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI King and Spanish mackerel (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI King and Spanish mackerel (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; King and Spanish mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 63.1 | 76.7 | 90.2 |
| Alternative weighting | 63.1 | 76.7 | 90.2 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Seafood 2022 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-king-spanish-mackerel-fresh-fish-wet-weight:fb6774b0d7e7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI King and Spanish mackerel (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI King and Spanish mackerel (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; King and Spanish mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 40 | 40 | 40 |
| Alternative weighting | 40 | 40 | 40 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Watanabe et al. 2017 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-king-spanish-mackerel-fresh-fish-basis-not-stated:a7547e960b10
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Horse mackerel, jacks and trevally (fresh or raw) tHg reference · 4 sampling families
Reference and scope
HMI Horse mackerel, jacks and trevally (fresh or raw) tHg reference · 4 sampling families. Fish, wet weight; Horse mackerel, jacks and trevally, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 107 | 110 | 351 |
| Alternative weighting | 107 | 110 | 351 |
20 reference units; 4 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 4 | 25% |
| EFSA 2012 | 3 | 25% |
| Olmedo et al. 2013 | 1 | 25% |
| Seafood 2022 | 12 | 25% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-horse-mackerel-jack-fresh-fish-wet-weight:9c88317f41ef
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Horse mackerel, jacks and trevally (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Horse mackerel, jacks and trevally (fresh or raw) tHg reference · 2 sampling families. Fish, basis not stated; Horse mackerel, jacks and trevally, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 60 | 100 |
| Alternative weighting | 20 | 60 | 100 |
8 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Lin et al. 2021 | 3 | 50% |
| Watanabe et al. 2017 | 5 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-horse-mackerel-jack-fresh-fish-basis-not-stated:5d95aa19788d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Horse mackerel, jacks and trevally (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Horse mackerel, jacks and trevally (fresh or raw) tHg reference · 2 sampling families. Fish, dry weight; Horse mackerel, jacks and trevally, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 296 | 1400 | 2460 |
| Alternative weighting | 296 | 1400 | 2460 |
16 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 4 | 50% |
| Seafood 2022 | 12 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-horse-mackerel-jack-fresh-fish-dry-weight:3db190120c08
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (canned) tHg reference · 1 sampling family
Reference and scope
HMI Herring (canned) tHg reference · 1 sampling family. Fish, basis not stated; Herring, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 86.4 | 93.2 | 100 |
| Alternative weighting | 86.4 | 93.2 | 100 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Pawlaczyk et al. 2020 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-herring-canned-fish-basis-not-stated:a801f9d1e6a5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Herring (fresh or raw) tHg reference · 3 sampling families. Fish, wet weight; Herring, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 32–33.9 (bounded) | 41.6 |
| Alternative weighting | 30 | 32–33.9 (bounded) | 41.6 |
19 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 15 | 33% |
| EFSA 2012 | 3 | 33% |
| Harding et al. 2018 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-herring-fresh-fish-wet-weight:19fedee3ba09
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Herring (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; Herring, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 35 | 40 |
| Alternative weighting | 30 | 35 | 40 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-herring-fresh-fish-basis-not-stated:2274c51f9511
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (smoked, dried, salted or fermented) tHg reference · 1 sampling family
Reference and scope
HMI Herring (smoked, dried, salted or fermented) tHg reference · 1 sampling family. Fish, basis not stated; Herring, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 25 | 40 |
| Alternative weighting | 10 | 25 | 40 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-herring-smoked-dried-salted-fermented-fish-basis-not-stated:4d1556203afe
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Sardine and pilchard (fresh or raw) tHg reference · 3 sampling families. Fish, wet weight; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 16–24.2 (bounded) | 30 | 34 |
| Alternative weighting | 16–24.2 (bounded) | 30 | 34 |
19 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 15 | 33% |
| EFSA 2012 | 3 | 33% |
| Olmedo et al. 2013 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-sardine-pilchard-fresh-fish-wet-weight:929b07b10f6e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Sardine and pilchard (fresh or raw) tHg reference · 3 sampling families. Fish, basis not stated; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 37 | 70 |
| Alternative weighting | 20 | 37 | 70 |
5 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Yamashita 2024 | 1 | 33% |
| European et al. 2004 | 3 | 33% |
| Watanabe et al. 2017 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-sardine-pilchard-fresh-fish-basis-not-stated:aea2ba64f651
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sprat (canned) tHg reference · 1 sampling family
Reference and scope
HMI Sprat (canned) tHg reference · 1 sampling family. Fish, basis not stated; Sprat, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 40 | 40 | 40 |
| Alternative weighting | 40 | 40 | 40 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-sprat-canned-fish-basis-not-stated:17bdadd7cce9
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sprat (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Sprat (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; Sprat, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 19 | 19 | 19 |
| Alternative weighting | 19 | 19 | 19 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-sprat-fresh-fish-wet-weight:cf13619b13de
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sprat (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Sprat (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; Sprat, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 20 | 20 |
| Alternative weighting | 20 | 20 | 20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-sprat-fresh-fish-basis-not-stated:2894215ac12b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sprat (smoked, dried, salted or fermented) tHg reference · 1 sampling family
Reference and scope
HMI Sprat (smoked, dried, salted or fermented) tHg reference · 1 sampling family. Fish, basis not stated; Sprat, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 50 | 50 | 50 |
| Alternative weighting | 50 | 50 | 50 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-sprat-smoked-dried-salted-fermented-fish-basis-not-stated:f5789ae7e069
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (canned) tHg reference · 1 sampling family
Reference and scope
HMI Anchovy (canned) tHg reference · 1 sampling family. Fish, wet weight; Anchovy, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 49 | 49 | 49 |
| Alternative weighting | 49 | 49 | 49 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-anchovy-canned-fish-wet-weight:cb9bf8939597
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (fish sauce) tHg reference · 1 sampling family
Reference and scope
HMI Anchovy (fish sauce) tHg reference · 1 sampling family. Fish, basis not stated; Anchovy, fish sauce; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1.5 | 4.1 | 26 |
| Alternative weighting | 1.5 | 4.1 | 26 |
9 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Diviš et al. 2020 | 9 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-anchovy-fish-sauce-fish-basis-not-stated:efb559230b75
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Anchovy (fresh or raw) tHg reference · 2 sampling families. Fish, wet weight; Anchovy, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 18 | 34 | 50 |
| Alternative weighting | 18 | 34 | 50 |
4 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-anchovy-fresh-fish-wet-weight:00dbc0c86bfc
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Anchovy (fresh or raw) tHg reference · 2 sampling families. Fish, basis not stated; Anchovy, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | 22.5–32.5 (bounded) | 50 |
| Alternative weighting | ≤20 | 22.5–32.5 (bounded) | 50 |
4 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 3 | 50% |
| Lin et al. 2021 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-anchovy-fresh-fish-basis-not-stated:a9afc9d5070c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shad, hilsa and other herrings (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Shad, hilsa and other herrings (fresh or raw) tHg reference · 2 sampling families. Fish, wet weight; Shad, hilsa and other herrings, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 75 | 124 | 173 |
| Alternative weighting | 75 | 124 | 173 |
4 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Eagles-Smith et al. 2016 | 1 | 50% |
| EFSA 2012 | 3 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-shad-other-clupeid-fresh-fish-wet-weight:be46bf6eb029
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shad, hilsa and other herrings (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Shad, hilsa and other herrings (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; Shad, hilsa and other herrings, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 20 | 20 |
| Alternative weighting | 20 | 20 | 20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Lin et al. 2021 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-shad-other-clupeid-fresh-fish-basis-not-stated:50c011ec7cf9
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (canned) tHg reference · 1 sampling family
Reference and scope
HMI Salmon (canned) tHg reference · 1 sampling family. Fish, wet weight; Salmon, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30.2 | 30.2 | 30.2 |
| Alternative weighting | 30.2 | 30.2 | 30.2 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-salmon-canned-fish-wet-weight:ba6f374dd8b7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (canned) tHg reference · 1 sampling family
Reference and scope
HMI Salmon (canned) tHg reference · 1 sampling family. Fish, basis not stated; Salmon, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 20 | 20 |
| Alternative weighting | 20 | 20 | 20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-salmon-canned-fish-basis-not-stated:6fa4a7e40b82
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (cooked) tHg reference · 1 sampling family
Reference and scope
HMI Salmon (cooked) tHg reference · 1 sampling family. Fish, wet weight; Salmon, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 18 | 18 | 18 |
| Alternative weighting | 18 | 18 | 18 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-salmon-cooked-fish-wet-weight:1a972eff39ad
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (fish product) tHg reference · 1 sampling family
Reference and scope
HMI Salmon (fish product) tHg reference · 1 sampling family. Fish, basis not stated; Salmon, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 30 | 30 |
| Alternative weighting | 30 | 30 | 30 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-salmon-fish-product-fish-basis-not-stated:2bbbd03c0605
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Salmon (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; Salmon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 120 | 134 | 149 |
| Alternative weighting | 120 | 134 | 149 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Selenium: 2021 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-salmon-fresh-fish-wet-weight:39f964f6bd32
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Salmon (fresh or raw) tHg reference · 2 sampling families. Fish, basis not stated; Salmon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 30 | 37 |
| Alternative weighting | 30 | 30 | 37 |
4 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 3 | 50% |
| Watanabe et al. 2017 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-salmon-fresh-fish-basis-not-stated:c3f10fbe8d43
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) tHg reference · 6 sampling families
Reference and scope
HMI Trout and char (fresh or raw) tHg reference · 6 sampling families. Fish, wet weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 37 | 178 | 660 |
| Alternative weighting | 37 | 178 | 660 |
25 reference units; 6 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 17 | 17% |
| Groleau et al. 2025 | 1 | 17% |
| Dietz et al. 2025 | 1 | 17% |
| Eagles-Smith et al. 2016 | 1 | 17% |
| EFSA 2012 | 3 | 17% |
| Selenium: 2021 | 2 | 17% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-trout-fresh-fish-wet-weight:1f9f559e9f37
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) tHg reference · 4 sampling families
Reference and scope
HMI Trout and char (fresh or raw) tHg reference · 4 sampling families. Fish, basis not stated; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5–10 (bounded) | 10–16.5 (bounded) | 16.5–20 (bounded) |
| Alternative weighting | 5–10 (bounded) | 10–16.5 (bounded) | 16.5–20 (bounded) |
6 reference units; 4 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Brodziak-Dopierala et al. 2023 | 2 | 25% |
| European et al. 2004 | 2 | 25% |
| Lin et al. 2021 | 1 | 25% |
| Watanabe et al. 2017 | 1 | 25% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-trout-fresh-fish-basis-not-stated:908004a13ec4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Whitefish and vendace (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Whitefish and vendace (fresh or raw) tHg reference · 3 sampling families. Fish, wet weight; Whitefish and vendace, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 70 | 75 | 80 |
| Alternative weighting | 70 | 75 | 80 |
6 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Concentration of… 2016 | 2 | 33% |
| Eagles-Smith et al. 2016 | 1 | 33% |
| EFSA 2012 | 3 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-whitefish-coregonid-fresh-fish-wet-weight:3b0a5abd8532
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (canned) tHg reference · 1 sampling family
Reference and scope
HMI Cod (canned) tHg reference · 1 sampling family. Fish, basis not stated; Cod, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 118 | 118 | 118 |
| Alternative weighting | 118 | 118 | 118 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Pawlaczyk et al. 2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-cod-canned-fish-basis-not-stated:de50de333d90
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (cooked) tHg reference · 2 sampling families
Reference and scope
HMI Cod (cooked) tHg reference · 2 sampling families. Fish, wet weight; Cod, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 26 | 56 | 76 |
| Alternative weighting | 26 | 56 | 76 |
9 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 50% |
| Iodine and Mercury… 2020 | 8 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-cod-cooked-fish-wet-weight:cf61f86129e1
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fish oil) tHg reference · 1 sampling family
Reference and scope
HMI Cod (fish oil) tHg reference · 1 sampling family. Fish, wet weight; Cod, fish oil; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1.5 | ≤4.5 | ≤15 |
| Alternative weighting | ≤1.5 | ≤4.5 | ≤15 |
6 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 6 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-cod-fish-oil-fish-wet-weight:39018c0c3482
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fish product) tHg reference · 1 sampling family
Reference and scope
HMI Cod (fish product) tHg reference · 1 sampling family. Fish, dry weight; Cod, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 19.4 | 19.4 | 19.4 |
| Alternative weighting | 19.4 | 19.4 | 19.4 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Maria et al. 2022 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-cod-fish-product-fish-dry-weight:e99ad78ba42c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Cod (fresh or raw) tHg reference · 2 sampling families. Fish, wet weight; Cod, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 28 | 28 | 33–42.5 (bounded) |
| Alternative weighting | 28 | 28 | 33–42.5 (bounded) |
18 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 17 | 50% |
| Harding et al. 2018 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-cod-fresh-fish-wet-weight:354005722a5f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Cod (fresh or raw) tHg reference · 2 sampling families. Fish, basis not stated; Cod, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 55 | 57.5 | 60 |
| Alternative weighting | 55 | 57.5 | 60 |
2 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 50% |
| Watanabe et al. 2017 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-cod-fresh-fish-basis-not-stated:0d4cc20adb74
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Haddock (fish product) tHg reference · 1 sampling family
Reference and scope
HMI Haddock (fish product) tHg reference · 1 sampling family. Fish, basis not stated; Haddock, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 40 | 40 | 40 |
| Alternative weighting | 40 | 40 | 40 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-haddock-fish-product-fish-basis-not-stated:5d0117c49540
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Haddock (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Haddock (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; Haddock, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 30 | 50 |
| Alternative weighting | 10 | 30 | 50 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-haddock-fresh-fish-basis-not-stated:fd19886a664e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Haddock (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Haddock (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; Haddock, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 26.7 | 26.7 | 26.7 |
| Alternative weighting | 26.7 | 26.7 | 26.7 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Harding et al. 2018 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-haddock-fresh-fish-wet-weight:27034f25fe5a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Pollock and saithe (fish product) tHg reference · 1 sampling family
Reference and scope
HMI Pollock and saithe (fish product) tHg reference · 1 sampling family. Fish, wet weight; Pollock and saithe, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 18 | 18 | 18 |
| Alternative weighting | 18 | 18 | 18 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Naess et al. 2020 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-pollock-saithe-fish-product-fish-wet-weight:2c9af7e4b921
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Pollock and saithe (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Pollock and saithe (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; Pollock and saithe, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 96 | 96 | 96 |
| Alternative weighting | 96 | 96 | 96 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Brodziak-Dopierala et al. 2023 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-pollock-saithe-fresh-fish-basis-not-stated:85dfd31556b7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Pollock and saithe (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Pollock and saithe (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; Pollock and saithe, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 15.6 | 15.6 | 15.6 |
| Alternative weighting | 15.6 | 15.6 | 15.6 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Harding et al. 2018 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-pollock-saithe-fresh-fish-wet-weight:b14a2785c367
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Whiting and blue whiting (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Whiting and blue whiting (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; Whiting and blue whiting, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 48 | 48 | 48 |
| Alternative weighting | 48 | 48 | 48 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-whiting-blue-whiting-fresh-fish-wet-weight:6f67b748a4c2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Whiting and blue whiting (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Whiting and blue whiting (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; Whiting and blue whiting, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 20 | 20 |
| Alternative weighting | 20 | 20 | 20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-whiting-blue-whiting-fresh-fish-basis-not-stated:0f2e0cd425ca
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hake (cooked) tHg reference · 1 sampling family
Reference and scope
HMI Hake (cooked) tHg reference · 1 sampling family. Fish, wet weight; Hake, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 64.5 | 78.5 | 88 |
| Alternative weighting | 64.5 | 78.5 | 88 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Products et al. 2019 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-hake-cooked-fish-wet-weight:25a6ada63671
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hake (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Hake (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; Hake, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 50 | 50 | 50 |
| Alternative weighting | 50 | 50 | 50 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-hake-fresh-fish-basis-not-stated:fea162067d99
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hake (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Hake (fresh or raw) tHg reference · 3 sampling families. Fish, wet weight; Hake, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 27.5 | 60.5 | 90 |
| Alternative weighting | 27.5 | 60.5 | 90 |
6 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 33% |
| Harding et al. 2018 | 1 | 33% |
| Olmedo et al. 2013 | 2 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-hake-fresh-fish-wet-weight:111984ff8887
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Ling, tusk and other cod-like fish (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Ling, tusk and other cod-like fish (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; Ling, tusk and other cod-like fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 98 | 98 | 98 |
| Alternative weighting | 98 | 98 | 98 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-other-gadiform-fresh-fish-wet-weight:7e773081d197
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Ling, tusk and other cod-like fish (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Ling, tusk and other cod-like fish (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; Ling, tusk and other cod-like fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 780 | 780 | 780 |
| Alternative weighting | 780 | 780 | 780 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Lin et al. 2021 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-other-gadiform-fresh-fish-basis-not-stated:d8ff4ffdf74e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Plaice, flounder, sole and turbot (fresh or raw) tHg reference · 3 sampling families. Fish, basis not stated; Plaice, flounder, sole and turbot, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 60 | 60 | 99 |
| Alternative weighting | 60 | 60 | 99 |
7 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Brodziak-Dopierala et al. 2023 | 1 | 33% |
| European et al. 2004 | 5 | 33% |
| Watanabe et al. 2017 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-plaice-flounder-sole-fresh-fish-basis-not-stated:7ac891a5ed6e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Plaice, flounder, sole and turbot (fresh or raw) tHg reference · 3 sampling families. Fish, wet weight; Plaice, flounder, sole and turbot, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 19 | 32.5 | 56 |
| Alternative weighting | 19 | 32.5 | 56 |
16 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 12 | 33% |
| Harding et al. 2018 | 2 | 33% |
| Olmedo et al. 2013 | 2 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-plaice-flounder-sole-fresh-fish-wet-weight:642c7cbebab6
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Halibut (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Halibut (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; Halibut, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 170 | 170 | 170 |
| Alternative weighting | 170 | 170 | 170 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-halibut-fresh-fish-wet-weight:a5167eba12a9
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bass and barramundi (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Sea bass and barramundi (fresh or raw) tHg reference · 1 sampling family. Fish, dry weight; Sea bass and barramundi, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 532 | 535 | 537 |
| Alternative weighting | 532 | 535 | 537 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Seafood 2022 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-sea-bass-fresh-fish-dry-weight:f47eff04ec00
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bass and barramundi (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Sea bass and barramundi (fresh or raw) tHg reference · 3 sampling families. Fish, wet weight; Sea bass and barramundi, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 79 | 104 | 118 |
| Alternative weighting | 79 | 104 | 118 |
9 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 6 | 33% |
| Olmedo et al. 2013 | 1 | 33% |
| Seafood 2022 | 2 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-sea-bass-fresh-fish-wet-weight:245c8c7553b8
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bream and porgies (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Sea bream and porgies (fresh or raw) tHg reference · 3 sampling families. Fish, wet weight; Sea bream and porgies, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 37 | 135 | 832 |
| Alternative weighting | 37 | 135 | 832 |
10 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 3 | 33% |
| EFSA 2012 | 6 | 33% |
| Olmedo et al. 2013 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-sea-bream-porgy-fresh-fish-wet-weight:f351960e8e70
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bream and porgies (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Sea bream and porgies (fresh or raw) tHg reference · 3 sampling families. Fish, basis not stated; Sea bream and porgies, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 60 | 148 | 200 |
| Alternative weighting | 60 | 148 | 200 |
4 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 2 | 33% |
| Lin et al. 2021 | 1 | 33% |
| Watanabe et al. 2017 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-sea-bream-porgy-fresh-fish-basis-not-stated:5d3edb9c2745
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Red mullet and goatfish (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Red mullet and goatfish (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; Red mullet and goatfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 67 | 67 | 67 |
| Alternative weighting | 67 | 67 | 67 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-red-mullet-goatfish-fresh-fish-wet-weight:7a5186c6cbdf
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Grey mullet (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Grey mullet (fresh or raw) tHg reference · 2 sampling families. Fish, basis not stated; Grey mullet, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 29.6 | 79.8 | 130 |
| Alternative weighting | 29.6 | 79.8 | 130 |
2 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Bakhshalizadeh et al. 2023 | 1 | 50% |
| European et al. 2004 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-grey-mullet-fresh-fish-basis-not-stated:9559d6bf1ed0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Grey mullet (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Grey mullet (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; Grey mullet, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 85 | 85 | 100 |
| Alternative weighting | 85 | 85 | 100 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-grey-mullet-fresh-fish-wet-weight:2eeab191de46
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Snapper (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Snapper (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; Snapper, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 78 | 78.9 | 207 |
| Alternative weighting | 78 | 78.9 | 207 |
5 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Seafood 2022 | 5 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-snapper-fresh-fish-wet-weight:9d0e09c7f484
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Snapper (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Snapper (fresh or raw) tHg reference · 1 sampling family. Fish, dry weight; Snapper, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 413 | 436 | 856 |
| Alternative weighting | 413 | 436 | 856 |
5 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Seafood 2022 | 5 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-snapper-fresh-fish-dry-weight:3f8a5949addc
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Grouper (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Grouper (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; Grouper, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 195 | 195 | 195 |
| Alternative weighting | 195 | 195 | 195 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-grouper-fresh-fish-wet-weight:f6f79f8a9cb5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Croaker and drum (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Croaker and drum (fresh or raw) tHg reference · 3 sampling families. Fish, wet weight; Croaker and drum, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 97.5 | 170 | 830 |
| Alternative weighting | 97.5 | 170 | 830 |
9 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 33% |
| Oliveira et al. 2022 | 2 | 33% |
| Seafood 2022 | 4 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-croaker-drum-fresh-fish-wet-weight:9d94886f75de
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Croaker and drum (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Croaker and drum (fresh or raw) tHg reference · 1 sampling family. Fish, dry weight; Croaker and drum, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 245 | 423 | 461 |
| Alternative weighting | 245 | 423 | 461 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Seafood 2022 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-croaker-drum-fresh-fish-dry-weight:1ccd3bdfe346
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Emperors and grunts (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Emperors and grunts (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; Emperors and grunts, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 90 | 90 | 90 |
| Alternative weighting | 90 | 90 | 90 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Christian et al. 2024 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-emperor-grunt-fresh-fish-wet-weight:31eb34f21a4d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hairtail and cutlassfish (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Hairtail and cutlassfish (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; Hairtail and cutlassfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 60 | 60 | 60 |
| Alternative weighting | 60 | 60 | 60 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Lin et al. 2021 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-hairtail-cutlassfish-fresh-fish-basis-not-stated:a749a54a69a4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Barracuda (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Barracuda (fresh or raw) tHg reference · 3 sampling families. Fish, wet weight; Barracuda, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 295 | 340 | 780 |
| Alternative weighting | 295 | 340 | 780 |
8 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 4 | 33% |
| Di et al. 2020 | 1 | 33% |
| EFSA 2012 | 3 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-barracuda-fresh-fish-wet-weight:fb705d07877d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Barracuda (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Barracuda (fresh or raw) tHg reference · 1 sampling family. Fish, dry weight; Barracuda, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 730 | 880 | 1280 |
| Alternative weighting | 730 | 880 | 1280 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-barracuda-fresh-fish-dry-weight:c67af8556d1c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mahi-mahi (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Mahi-mahi (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; Mahi-mahi, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 20 | 20 |
| Alternative weighting | 20 | 20 | 20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Lin et al. 2021 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-mahi-mahi-fresh-fish-basis-not-stated:44ed026840a4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Scorpionfish and rockfish (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Scorpionfish and rockfish (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; Scorpionfish and rockfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 422 | 422 | 422 |
| Alternative weighting | 422 | 422 | 422 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-scorpionfish-rockfish-fresh-fish-wet-weight:cd04dd86d623
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anglerfish and monkfish (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Anglerfish and monkfish (fresh or raw) tHg reference · 2 sampling families. Fish, wet weight; Anglerfish and monkfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 78 | 129 | 158 |
| Alternative weighting | 78 | 129 | 158 |
4 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-anglerfish-monkfish-fresh-fish-wet-weight:5fd4a3354078
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Gurnard (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Gurnard (fresh or raw) tHg reference · 2 sampling families. Fish, wet weight; Gurnard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 75 | 368 | 660 |
| Alternative weighting | 75 | 368 | 660 |
4 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 1 | 50% |
| EFSA 2012 | 3 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-gurnard-fresh-fish-wet-weight:2e7c9f19ea65
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Gurnard (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Gurnard (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; Gurnard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 160 | 160 | 160 |
| Alternative weighting | 160 | 160 | 160 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-gurnard-fresh-fish-basis-not-stated:369ccaf410b7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Eel (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Eel (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; Eel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 130 | 130 | 130 |
| Alternative weighting | 130 | 130 | 130 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-eel-fresh-fish-wet-weight:e8117ac226b7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Eel (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Eel (fresh or raw) tHg reference · 2 sampling families. Fish, basis not stated; Eel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 60 | 80 | 80 |
| Alternative weighting | 60 | 80 | 80 |
3 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 2 | 50% |
| Lin et al. 2021 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-eel-fresh-fish-basis-not-stated:3e61c30cffce
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sturgeon (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Sturgeon (fresh or raw) tHg reference · 1 sampling family. Fish, wet weight; Sturgeon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 36 | 61 | 79 |
| Alternative weighting | 36 | 61 | 79 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-sturgeon-fresh-fish-wet-weight:08a9fef0818b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sturgeon (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Sturgeon (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; Sturgeon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤20 | ≤20 |
| Alternative weighting | ≤20 | ≤20 | ≤20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Lin et al. 2021 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-sturgeon-fresh-fish-basis-not-stated:7b2583e0c30b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other marine fish (cooked) tHg reference · 1 sampling family
Reference and scope
HMI Other marine fish (cooked) tHg reference · 1 sampling family. Fish, wet weight; Other marine fish, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 153 | 194 | 263 |
| Alternative weighting | 153 | 194 | 263 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Products et al. 2019 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-other-marine-finfish-cooked-fish-wet-weight:5b1809dec913
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other marine fish (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Other marine fish (fresh or raw) tHg reference · 2 sampling families. Fish, basis not stated; Other marine fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 60 | 80 | 120 |
| Alternative weighting | 60 | 80 | 120 |
4 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Lin et al. 2021 | 3 | 50% |
| Watanabe et al. 2017 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-other-marine-finfish-fresh-fish-basis-not-stated:e969cc3d49c5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other marine fish (fresh or raw) tHg reference · 5 sampling families
Reference and scope
HMI Other marine fish (fresh or raw) tHg reference · 5 sampling families. Fish, wet weight; Other marine fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10.8 | 84.9 | 100 |
| Alternative weighting | 10.8 | 84.9 | 100 |
45 reference units; 5 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Christian et al. 2024 | 2 | 20% |
| Diet shifts drive… 2025 | 4 | 20% |
| EFSA 2012 | 30 | 20% |
| Harding et al. 2018 | 1 | 20% |
| Seafood 2022 | 8 | 20% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-other-marine-finfish-fresh-fish-wet-weight:9c558a1fb534
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other marine fish (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Other marine fish (fresh or raw) tHg reference · 1 sampling family. Fish, dry weight; Other marine fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 341 | 445 | 606 |
| Alternative weighting | 341 | 445 | 606 |
8 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Seafood 2022 | 8 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-other-marine-finfish-fresh-fish-dry-weight:f92475828a0d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tilapia (cooked) tHg reference · 1 sampling family
Reference and scope
HMI Tilapia (cooked) tHg reference · 1 sampling family. Fish, wet weight; Tilapia, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5.1 | 5.1 | 5.1 |
| Alternative weighting | 5.1 | 5.1 | 5.1 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-tilapia-cooked-fish-wet-weight:5d4f6ae85529
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tilapia (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Tilapia (fresh or raw) tHg reference · 1 sampling family. Fish, dry weight; Tilapia, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 8 | 11 | 14 |
| Alternative weighting | 8 | 11 | 14 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Shumba et al. 2025 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-tilapia-fresh-fish-dry-weight:2c57f18cf102
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (fresh or raw) tHg reference · 5 sampling families
Reference and scope
HMI Carp and other cyprinids (fresh or raw) tHg reference · 5 sampling families. Fish, wet weight; Carp and other cyprinids, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 29 | 78 | 96 |
| Alternative weighting | 29 | 78 | 96 |
19 reference units; 5 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Concentration of… 2016 | 2 | 20% |
| Eagles-Smith et al. 2016 | 1 | 20% |
| EFSA 2012 | 9 | 20% |
| Rusko et al. 2026 | 3 | 20% |
| Tissue-Specific Mercury… 2026 | 4 | 20% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
- Concentration of… 2016
- Eagles-Smith et al. 2016
- EFSA 2012
- Rusko et al. 2026
- Tissue-Specific Mercury… 2026
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-carp-cyprinid-fresh-fish-wet-weight:6511a68c4e8e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Catfish (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Catfish (fresh or raw) tHg reference · 3 sampling families. Fish, wet weight; Catfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 44 | 87.3 | 645 |
| Alternative weighting | 44 | 87.3 | 645 |
7 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 4 | 33% |
| Selenium: 2021 | 2 | 33% |
| Tissue-Specific Mercury… 2026 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-catfish-fresh-fish-wet-weight:b8e9b502cae8
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Catfish (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Catfish (fresh or raw) tHg reference · 2 sampling families. Fish, basis not stated; Catfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 56 | 58 | 58 |
| Alternative weighting | 56 | 58 | 58 |
95 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Dataset of concentration… 2020 | 94 | 50% |
| Brodziak-Dopierala et al. 2023 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-catfish-fresh-fish-basis-not-stated:92e24f8e43bc
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Catfish (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Catfish (fresh or raw) tHg reference · 3 sampling families. Fish, dry weight; Catfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 334 | 2800 | 3940 |
| Alternative weighting | 334 | 2800 | 3940 |
7 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 4 | 33% |
| Characterized et al. 2025 | 2 | 33% |
| Seafood 2022 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-catfish-fresh-fish-dry-weight:fd59ec9885ff
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Pike (fresh or raw) tHg reference · 5 sampling families
Reference and scope
HMI Pike (fresh or raw) tHg reference · 5 sampling families. Fish, wet weight; Pike, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 187 | 240 | 290 |
| Alternative weighting | 187 | 240 | 290 |
8 reference units; 5 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Concentration of… 2016 | 1 | 20% |
| Eagles-Smith et al. 2016 | 1 | 20% |
| EFSA 2012 | 3 | 20% |
| Rusko et al. 2026 | 1 | 20% |
| total mercury (THg),… 2026 | 2 | 20% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-pike-fresh-fish-wet-weight:4e0c93b52d77
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Perch, walleye and zander (fresh or raw) tHg reference · 6 sampling families
Reference and scope
HMI Perch, walleye and zander (fresh or raw) tHg reference · 6 sampling families. Fish, wet weight; Perch, walleye and zander, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 127 | 147 | 238 |
| Alternative weighting | 127 | 147 | 238 |
10 reference units; 6 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Concentration of… 2016 | 1 | 17% |
| Eagles-Smith et al. 2016 | 1 | 17% |
| EFSA 2012 | 3 | 17% |
| Rusko et al. 2026 | 2 | 17% |
| Selenium: 2021 | 2 | 17% |
| Tissue-Specific Mercury… 2026 | 1 | 17% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
- Concentration of… 2016
- Eagles-Smith et al. 2016
- EFSA 2012
- Rusko et al. 2026
- Selenium: 2021
- Tissue-Specific Mercury… 2026
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-perch-walleye-fresh-fish-wet-weight:10b79d508e61
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Perch, walleye and zander (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Perch, walleye and zander (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; Perch, walleye and zander, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 129 | 129 | 129 |
| Alternative weighting | 129 | 129 | 129 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-perch-walleye-fresh-fish-basis-not-stated:db0fe611a544
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Black bass and sunfish (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Black bass and sunfish (fresh or raw) tHg reference · 2 sampling families. Fish, wet weight; Black bass and sunfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 152 | 195 | 245 |
| Alternative weighting | 152 | 195 | 245 |
6 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Eagles-Smith et al. 2016 | 2 | 50% |
| Selenium: 2021 | 4 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-black-bass-sunfish-fresh-fish-wet-weight:e097befc0cff
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other cichlids (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Other cichlids (fresh or raw) tHg reference · 2 sampling families. Fish, wet weight; Other cichlids, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 32 | 161 | 440 |
| Alternative weighting | 32 | 161 | 440 |
3 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Eagles-Smith et al. 2016 | 1 | 50% |
| Oliveira et al. 2022 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-cichlid-other-fresh-fish-wet-weight:58b8fb05b5f2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other cichlids (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Other cichlids (fresh or raw) tHg reference · 1 sampling family. Fish, basis not stated; Other cichlids, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 87.9 | 166 | 293 |
| Alternative weighting | 87.9 | 166 | 293 |
114 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Dataset of concentration… 2020 | 114 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-cichlid-other-fresh-fish-basis-not-stated:e3b7fcc064e2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other freshwater fish (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Other freshwater fish (fresh or raw) tHg reference · 2 sampling families. Fish, wet weight; Other freshwater fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 128 | 128 | 340 |
| Alternative weighting | 128 | 128 | 340 |
7 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Eagles-Smith et al. 2016 | 6 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-other-freshwater-finfish-fresh-fish-wet-weight:72914ad94e4e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other freshwater fish (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Other freshwater fish (fresh or raw) tHg reference · 3 sampling families. Fish, basis not stated; Other freshwater fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 40 | 60 | 208 |
| Alternative weighting | 40 | 60 | 208 |
117 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Dataset of concentration… 2020 | 115 | 33% |
| European et al. 2004 | 1 | 33% |
| Lin et al. 2021 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-other-freshwater-finfish-fresh-fish-basis-not-stated:eb7a474de3e6
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other freshwater fish (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Other freshwater fish (fresh or raw) tHg reference · 1 sampling family. Fish, dry weight; Other freshwater fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 46.3 | 123 | 260 |
| Alternative weighting | 46.3 | 123 | 260 |
8 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| contrasting levels of… 2025 | 8 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-other-freshwater-finfish-fresh-fish-dry-weight:172924aa8253
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (canned) tHg reference · 2 sampling families
Reference and scope
HMI Marine fish, species not stated (canned) tHg reference · 2 sampling families. Fish, basis not stated; Marine fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 24.1 | 37 | 50 |
| Alternative weighting | 24.1 | 37 | 50 |
2 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 50% |
| Pawlaczyk et al. 2020 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-fish-unspecified-marine-canned-fish-basis-not-stated:e3d213fd88a0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Marine fish, species not stated (fresh or raw) tHg reference · 2 sampling families. Fish, basis not stated; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 265 | 755 | 1050 |
| Alternative weighting | 265 | 755 | 1050 |
3 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 50% |
| Blanco et al. 2023 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-fish-unspecified-marine-fresh-fish-basis-not-stated:5925051a3bb2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) tHg reference · 2 sampling families
Reference and scope
HMI Marine fish, species not stated (fresh or raw) tHg reference · 2 sampling families. Fish, wet weight; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 54 | 63 | 230 |
| Alternative weighting | 54 | 63 | 230 |
6 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 50% |
| Garofalo et al. 2025 | 3 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-fish-unspecified-marine-fresh-fish-wet-weight:09bae0f53363
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (fresh or raw) tHg reference · 4 sampling families
Reference and scope
HMI Freshwater fish, species not stated (fresh or raw) tHg reference · 4 sampling families. Fish, wet weight; Freshwater fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 50 | 180 | 435 |
| Alternative weighting | 50 | 180 | 435 |
9 reference units; 4 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Escobar-Camacho et al. 2024 | 2 | 25% |
| Garofalo et al. 2025 | 1 | 25% |
| Health Risk Assessment… 2022 | 4 | 25% |
| Stahl et al. 2023 | 2 | 25% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-fish-unspecified-freshwater-fresh-fish-wet-weight:f4bd83e96306
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) tHg reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (canned) tHg reference · 1 sampling family. Fish, wet weight; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 207 | 207 | 207 |
| Alternative weighting | 207 | 207 | 207 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-fish-unspecified-canned-fish-wet-weight:ded44eabd0d1
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) tHg reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (canned) tHg reference · 1 sampling family. Fish, basis not stated; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 33.4 | 36.6 | 44.7 |
| Alternative weighting | 33.4 | 36.6 | 44.7 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Pawlaczyk et al. 2020 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-fish-unspecified-canned-fish-basis-not-stated:cfdf206628ca
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (cooked) tHg reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (cooked) tHg reference · 1 sampling family. Fish, wet weight; Fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 69.8 | 70.8 | 71.9 |
| Alternative weighting | 69.8 | 70.8 | 71.9 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-fish-unspecified-cooked-fish-wet-weight:033a2b4a9d44
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish oil) tHg reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (fish oil) tHg reference · 2 sampling families. Fish, wet weight; Fish, species not stated, fish oil; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤0.625 | 0.15–1.4 (bounded) | 1.05–3.52 (bounded) |
| Alternative weighting | ≤0.625 | 0.15–1.4 (bounded) | 1.05–3.52 (bounded) |
9 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 6 | 50% |
| EFSA 2012 | 3 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-fish-unspecified-fish-oil-fish-wet-weight:cf69004b64fc
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) tHg reference · 6 sampling families
Reference and scope
HMI Fish, species not stated (fish product) tHg reference · 6 sampling families. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 6–6.1 (bounded) | 22 | 53.7 |
| Alternative weighting | 6–6.1 (bounded) | 22 | 53.7 |
64 reference units; 6 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 28 | 17% |
| FDA TDS FY2018–FY2020 | 1 | 17% |
| Baxter et al. 2015 | 2 | 17% |
| Products et al. 2019 | 26 | 17% |
| EFSA 2012 | 6 | 17% |
| Food 2011 | 1 | 17% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-fish-unspecified-fish-product-fish-wet-weight:a0fbd10a9fc0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) tHg reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish product) tHg reference · 1 sampling family. Fish, basis not stated; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 30 | 30 |
| Alternative weighting | 20 | 30 | 30 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-fish-unspecified-fish-product-fish-basis-not-stated:e5d0f9ffada7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) tHg reference · 5 sampling families
Reference and scope
HMI Fish, species not stated (fresh or raw) tHg reference · 5 sampling families. Fish, wet weight; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 57 | 61.6–68 (bounded) | 108 |
| Alternative weighting | 57 | 61.6–68 (bounded) | 108 |
37 reference units; 5 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 17 | 20% |
| Eagles-Smith et al. 2016 | 1 | 20% |
| EFSA 2012 | 12 | 20% |
| Health Risk Assessment… 2022 | 4 | 20% |
| Seafood 2022 | 3 | 20% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-fish-unspecified-fresh-fish-wet-weight:829de798a0c5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) tHg reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fresh or raw) tHg reference · 1 sampling family. Fish, dry weight; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 310 | 420 | 460 |
| Alternative weighting | 310 | 420 | 460 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Seafood 2022 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-fish-unspecified-fresh-fish-dry-weight:56eb635fce4c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) tHg reference · 3 sampling families
Reference and scope
HMI Fish, species not stated (fresh or raw) tHg reference · 3 sampling families. Fish, basis not stated; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 50 | 60 | 110 |
| Alternative weighting | 50 | 60 | 110 |
8 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 5 | 33% |
| Blanco et al. 2023 | 1 | 33% |
| Brodziak-Dopierala et al. 2023 | 2 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-fish-unspecified-fresh-fish-basis-not-stated:59df8533c9ba
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (smoked, dried, salted or fermented) tHg reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (smoked, dried, salted or fermented) tHg reference · 1 sampling family. Fish, basis not stated; Fish, species not stated, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1260 | 1260 | 1260 |
| Alternative weighting | 1260 | 1260 | 1260 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tHg-fish-unspecified-smoked-dried-salted-fermented-fish-basis-not-stated:c62d87dde20e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (canned) MeHg reference · 1 sampling family
Reference and scope
HMI Tuna (canned) MeHg reference · 1 sampling family. Fish, basis not stated; Tuna, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 583 | 604 | 624 |
| Alternative weighting | 583 | 604 | 624 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Carter et al. 2025 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-tuna-canned-fish-basis-not-stated:890d32f506da
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (cooked) MeHg reference · 1 sampling family
Reference and scope
HMI Tuna (cooked) MeHg reference · 1 sampling family. Fish, wet weight; Tuna, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 60 | 180 | 217 |
| Alternative weighting | 60 | 180 | 217 |
5 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 5 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-tuna-cooked-fish-wet-weight:3960491de4e0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) MeHg reference · 2 sampling families
Reference and scope
HMI Tuna (fresh or raw) MeHg reference · 2 sampling families. Fish, wet weight; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 133 | 133 | 196 |
| Alternative weighting | 133 | 133 | 196 |
12 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 9 | 50% |
| EFSA 2012 | 3 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-tuna-fresh-fish-wet-weight:6eeecf641a39
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Tuna (fresh or raw) MeHg reference · 1 sampling family. Fish, basis not stated; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 240 | 325 | 500 |
| Alternative weighting | 240 | 325 | 500 |
6 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Watanabe et al. 2017 | 6 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-tuna-fresh-fish-basis-not-stated:4b381c726306
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Swordfish (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Swordfish (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Swordfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 795 | 795 | 795 |
| Alternative weighting | 795 | 795 | 795 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-swordfish-fresh-fish-wet-weight:d753756135db
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Swordfish (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Swordfish (fresh or raw) MeHg reference · 1 sampling family. Fish, basis not stated; Swordfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1420 | 1420 | 1420 |
| Alternative weighting | 1420 | 1420 | 1420 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Watanabe et al. 2017 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-swordfish-fresh-fish-basis-not-stated:df8d1e23fd86
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shark (fresh or raw) MeHg reference · 3 sampling families
Reference and scope
HMI Shark (fresh or raw) MeHg reference · 3 sampling families. Fish, wet weight; Shark, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 79.9 | 102 | 1510 |
| Alternative weighting | 79.9 | 102 | 1510 |
29 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Sang et al. 2019 | 25 | 33% |
| EFSA 2012 | 3 | 33% |
| Harding et al. 2018 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-shark-fresh-fish-wet-weight:977ed95f0db2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (cooked) MeHg reference · 1 sampling family
Reference and scope
HMI Mackerel (cooked) MeHg reference · 1 sampling family. Fish, wet weight; Mackerel, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 80 | 125 | 170 |
| Alternative weighting | 80 | 125 | 170 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-mackerel-cooked-fish-wet-weight:61a01689a8c7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) MeHg reference · 3 sampling families
Reference and scope
HMI Mackerel (fresh or raw) MeHg reference · 3 sampling families. Fish, wet weight; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 16.5 | 29–31.5 (bounded) | 34–40.5 (bounded) |
| Alternative weighting | 16.5 | 29–31.5 (bounded) | 34–40.5 (bounded) |
13 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 9 | 33% |
| EFSA 2012 | 3 | 33% |
| Harding et al. 2018 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-mackerel-fresh-fish-wet-weight:ef7e0bca7eab
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Mackerel (fresh or raw) MeHg reference · 1 sampling family. Fish, basis not stated; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 150 | 150 | 150 |
| Alternative weighting | 150 | 150 | 150 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Watanabe et al. 2017 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-mackerel-fresh-fish-basis-not-stated:99128189e323
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI King and Spanish mackerel (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI King and Spanish mackerel (fresh or raw) MeHg reference · 1 sampling family. Fish, basis not stated; King and Spanish mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 40 | 40 | 40 |
| Alternative weighting | 40 | 40 | 40 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Watanabe et al. 2017 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-king-spanish-mackerel-fresh-fish-basis-not-stated:ec473c8e4079
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Horse mackerel, jacks and trevally (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Horse mackerel, jacks and trevally (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Horse mackerel, jacks and trevally, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 320 | 330 | 340 |
| Alternative weighting | 320 | 330 | 340 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-horse-mackerel-jack-fresh-fish-wet-weight:bbc834031905
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Horse mackerel, jacks and trevally (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Horse mackerel, jacks and trevally (fresh or raw) MeHg reference · 1 sampling family. Fish, dry weight; Horse mackerel, jacks and trevally, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1290 | 1330 | 1360 |
| Alternative weighting | 1290 | 1330 | 1360 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-horse-mackerel-jack-fresh-fish-dry-weight:692e4d65abbf
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Horse mackerel, jacks and trevally (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Horse mackerel, jacks and trevally (fresh or raw) MeHg reference · 1 sampling family. Fish, basis not stated; Horse mackerel, jacks and trevally, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 60 | 90 | 140 |
| Alternative weighting | 60 | 90 | 140 |
5 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Watanabe et al. 2017 | 5 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-horse-mackerel-jack-fresh-fish-basis-not-stated:eb8d2c7bb9ed
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (cooked) MeHg reference · 1 sampling family
Reference and scope
HMI Herring (cooked) MeHg reference · 1 sampling family. Fish, wet weight; Herring, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤14 | 60 | 61 |
| Alternative weighting | ≤14 | 60 | 61 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-herring-cooked-fish-wet-weight:5dcd1dd9776c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (fresh or raw) MeHg reference · 3 sampling families
Reference and scope
HMI Herring (fresh or raw) MeHg reference · 3 sampling families. Fish, wet weight; Herring, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 26 | 35.5–37.5 (bounded) | 38 |
| Alternative weighting | 26 | 35.5–37.5 (bounded) | 38 |
8 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 4 | 33% |
| EFSA 2012 | 3 | 33% |
| Harding et al. 2018 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-herring-fresh-fish-wet-weight:4a0234e27a61
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (cooked) MeHg reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (cooked) MeHg reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤14 | ≤14 | ≤14 |
| Alternative weighting | ≤14 | ≤14 | ≤14 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-sardine-pilchard-cooked-fish-wet-weight:6222bc4f09f6
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) MeHg reference · 2 sampling families
Reference and scope
HMI Sardine and pilchard (fresh or raw) MeHg reference · 2 sampling families. Fish, wet weight; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | 25.5–40 (bounded) | 50–100 (bounded) |
| Alternative weighting | ≤20 | 25.5–40 (bounded) | 50–100 (bounded) |
12 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 9 | 50% |
| EFSA 2012 | 3 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-sardine-pilchard-fresh-fish-wet-weight:ac5bd75c509e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (fresh or raw) MeHg reference · 1 sampling family. Fish, basis not stated; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 20 | 20 |
| Alternative weighting | 20 | 20 | 20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Watanabe et al. 2017 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-sardine-pilchard-fresh-fish-basis-not-stated:05c9a7df2249
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sprat (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Sprat (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Sprat, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 8 | 8 | 8 |
| Alternative weighting | 8 | 8 | 8 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-sprat-fresh-fish-wet-weight:8bc0b4254ff0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Anchovy (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Anchovy, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 0 | 50 | 100 |
| Alternative weighting | 0 | 50 | 100 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-anchovy-fresh-fish-wet-weight:581b96801fab
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (cooked) MeHg reference · 1 sampling family
Reference and scope
HMI Salmon (cooked) MeHg reference · 1 sampling family. Fish, wet weight; Salmon, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤14 | ≤14 | 19.3 |
| Alternative weighting | ≤14 | ≤14 | 19.3 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-salmon-cooked-fish-wet-weight:e25a63d54035
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Salmon (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Salmon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 30 | 30 |
| Alternative weighting | 30 | 30 | 30 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-salmon-fresh-fish-wet-weight:b30615220806
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Salmon (fresh or raw) MeHg reference · 1 sampling family. Fish, basis not stated; Salmon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 30 | 30 |
| Alternative weighting | 30 | 30 | 30 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Watanabe et al. 2017 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-salmon-fresh-fish-basis-not-stated:4d67a78f8852
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (cooked) MeHg reference · 1 sampling family
Reference and scope
HMI Trout and char (cooked) MeHg reference · 1 sampling family. Fish, wet weight; Trout and char, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 19.5 | 19.5 | 19.5 |
| Alternative weighting | 19.5 | 19.5 | 19.5 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-trout-cooked-fish-wet-weight:af532e00d73e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10.8–17.5 (bounded) | 19.5–21 (bounded) | 21–23.4 (bounded) |
| Alternative weighting | 10.8–17.5 (bounded) | 19.5–21 (bounded) | 21–23.4 (bounded) |
13 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 13 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-trout-fresh-fish-wet-weight:6ac76e0813a5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) MeHg reference · 1 sampling family. Fish, basis not stated; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 10 |
| Alternative weighting | 10 | 10 | 10 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Watanabe et al. 2017 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-trout-fresh-fish-basis-not-stated:b8c61d132a6d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (cooked) MeHg reference · 1 sampling family
Reference and scope
HMI Cod (cooked) MeHg reference · 1 sampling family. Fish, wet weight; Cod, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 44.5 | 44.5 | 44.5 |
| Alternative weighting | 44.5 | 44.5 | 44.5 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-cod-cooked-fish-wet-weight:20b3e8fc0058
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fresh or raw) MeHg reference · 2 sampling families
Reference and scope
HMI Cod (fresh or raw) MeHg reference · 2 sampling families. Fish, wet weight; Cod, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 26 | 26 | 38.2–50 (bounded) |
| Alternative weighting | 26 | 26 | 38.2–50 (bounded) |
8 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 7 | 50% |
| Harding et al. 2018 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-cod-fresh-fish-wet-weight:29227342ee92
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Cod (fresh or raw) MeHg reference · 1 sampling family. Fish, basis not stated; Cod, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 60 | 60 | 60 |
| Alternative weighting | 60 | 60 | 60 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Watanabe et al. 2017 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-cod-fresh-fish-basis-not-stated:836b1f2b5bdd
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Haddock (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Haddock (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Haddock, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 14.5 | 14.5 | 14.5 |
| Alternative weighting | 14.5 | 14.5 | 14.5 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Harding et al. 2018 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-haddock-fresh-fish-wet-weight:2c4571069820
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Pollock and saithe (cooked) MeHg reference · 1 sampling family
Reference and scope
HMI Pollock and saithe (cooked) MeHg reference · 1 sampling family. Fish, wet weight; Pollock and saithe, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 8–9.5 (bounded) | 8–9.5 (bounded) | 8–9.5 (bounded) |
| Alternative weighting | 8–9.5 (bounded) | 8–9.5 (bounded) | 8–9.5 (bounded) |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-pollock-saithe-cooked-fish-wet-weight:206d40e36759
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Pollock and saithe (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Pollock and saithe (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Pollock and saithe, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 14.2 | 14.2 | 14.2 |
| Alternative weighting | 14.2 | 14.2 | 14.2 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Harding et al. 2018 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-pollock-saithe-fresh-fish-wet-weight:10fae420467e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hake (fresh or raw) MeHg reference · 2 sampling families
Reference and scope
HMI Hake (fresh or raw) MeHg reference · 2 sampling families. Fish, wet weight; Hake, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 25.4 | 25.4 | 50 |
| Alternative weighting | 25.4 | 25.4 | 50 |
4 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 50% |
| Harding et al. 2018 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-hake-fresh-fish-wet-weight:cedab3e21a8f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (fresh or raw) MeHg reference · 2 sampling families
Reference and scope
HMI Plaice, flounder, sole and turbot (fresh or raw) MeHg reference · 2 sampling families. Fish, wet weight; Plaice, flounder, sole and turbot, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 18.7 | 36.2 | 50 |
| Alternative weighting | 18.7 | 36.2 | 50 |
5 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 50% |
| Harding et al. 2018 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-plaice-flounder-sole-fresh-fish-wet-weight:aaf3ec805dfd
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Plaice, flounder, sole and turbot (fresh or raw) MeHg reference · 1 sampling family. Fish, basis not stated; Plaice, flounder, sole and turbot, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 50 | 50 | 50 |
| Alternative weighting | 50 | 50 | 50 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Watanabe et al. 2017 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-plaice-flounder-sole-fresh-fish-basis-not-stated:81031e922309
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Halibut (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Halibut (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Halibut, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 79 | 79 | 79 |
| Alternative weighting | 79 | 79 | 79 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-halibut-fresh-fish-wet-weight:ababc3550878
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bass and barramundi (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Sea bass and barramundi (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Sea bass and barramundi, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 0 | 50 | 100 |
| Alternative weighting | 0 | 50 | 100 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-sea-bass-fresh-fish-wet-weight:4b40b15bde55
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bream and porgies (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Sea bream and porgies (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Sea bream and porgies, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 51 | 76 | 101 |
| Alternative weighting | 51 | 76 | 101 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-sea-bream-porgy-fresh-fish-wet-weight:3a65083d95a5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bream and porgies (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Sea bream and porgies (fresh or raw) MeHg reference · 1 sampling family. Fish, basis not stated; Sea bream and porgies, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 170 | 170 | 170 |
| Alternative weighting | 170 | 170 | 170 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Watanabe et al. 2017 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-sea-bream-porgy-fresh-fish-basis-not-stated:79f9d72dc017
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Grey mullet (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Grey mullet (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Grey mullet, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 0 | 50 | 100 |
| Alternative weighting | 0 | 50 | 100 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-grey-mullet-fresh-fish-wet-weight:4445aba9ed79
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Barracuda (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Barracuda (fresh or raw) MeHg reference · 1 sampling family. Fish, dry weight; Barracuda, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 620 | 680 | 740 |
| Alternative weighting | 620 | 680 | 740 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-barracuda-fresh-fish-dry-weight:38c917db2ffe
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Barracuda (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Barracuda (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Barracuda, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 160 | 175 | 190 |
| Alternative weighting | 160 | 175 | 190 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-barracuda-fresh-fish-wet-weight:b9d978ee6826
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anglerfish and monkfish (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Anglerfish and monkfish (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Anglerfish and monkfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 148 | 148 | 148 |
| Alternative weighting | 148 | 148 | 148 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-anglerfish-monkfish-fresh-fish-wet-weight:0c05784eb420
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Eel (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Eel (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Eel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 93 | 93 | 93 |
| Alternative weighting | 93 | 93 | 93 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-eel-fresh-fish-wet-weight:9eaa7bc26d78
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other marine fish (fresh or raw) MeHg reference · 2 sampling families
Reference and scope
HMI Other marine fish (fresh or raw) MeHg reference · 2 sampling families. Fish, basis not stated; Other marine fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 60 | 685 | 1310 |
| Alternative weighting | 60 | 685 | 1310 |
2 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| A Study on Total… 2013 | 1 | 50% |
| Watanabe et al. 2017 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-other-marine-finfish-fresh-fish-basis-not-stated:c7b16e09d90a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other marine fish (fresh or raw) MeHg reference · 3 sampling families
Reference and scope
HMI Other marine fish (fresh or raw) MeHg reference · 3 sampling families. Fish, wet weight; Other marine fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 73 | 75.1 | 75.8 |
| Alternative weighting | 73 | 75.1 | 75.8 |
9 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Diet shifts drive… 2025 | 2 | 33% |
| EFSA 2012 | 6 | 33% |
| Harding et al. 2018 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-other-marine-finfish-fresh-fish-wet-weight:962cb751e385
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Carp and other cyprinids, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 10 |
| Alternative weighting | 10 | 10 | 10 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-carp-cyprinid-fresh-fish-wet-weight:2a52da4528a7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Catfish (fresh or raw) MeHg reference · 2 sampling families
Reference and scope
HMI Catfish (fresh or raw) MeHg reference · 2 sampling families. Fish, dry weight; Catfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1780 | 2810 | 3790 |
| Alternative weighting | 1780 | 2810 | 3790 |
3 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 2 | 50% |
| Characterized et al. 2025 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-catfish-fresh-fish-dry-weight:1c8333c26550
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Catfish (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Catfish (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Catfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 430 | 445 | 460 |
| Alternative weighting | 430 | 445 | 460 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-catfish-fresh-fish-wet-weight:15332d5904a8
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Perch, walleye and zander (fresh or raw) MeHg reference · 1 sampling family
Reference and scope
HMI Perch, walleye and zander (fresh or raw) MeHg reference · 1 sampling family. Fish, wet weight; Perch, walleye and zander, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 56 | 56 | 56 |
| Alternative weighting | 56 | 56 | 56 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2012 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-perch-walleye-fresh-fish-wet-weight:fe1617898468
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) MeHg reference · 2 sampling families
Reference and scope
HMI Marine fish, species not stated (fresh or raw) MeHg reference · 2 sampling families. Fish, wet weight; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 55 | 360 |
| Alternative weighting | 10 | 55 | 360 |
10 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 7 | 50% |
| EFSA 2012 | 3 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-fish-unspecified-marine-fresh-fish-wet-weight:e83e81d32259
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (cooked) MeHg reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (cooked) MeHg reference · 1 sampling family. Fish, wet weight; Freshwater fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 75–82 (bounded) | 75–82 (bounded) | 75–82 (bounded) |
| Alternative weighting | 75–82 (bounded) | 75–82 (bounded) | 75–82 (bounded) |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-fish-unspecified-freshwater-cooked-fish-wet-weight:8a6b5eff0068
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (cooked) MeHg reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (cooked) MeHg reference · 1 sampling family. Fish, wet weight; Fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤14 | 35–42 (bounded) | 77.8 |
| Alternative weighting | ≤14 | 35–42 (bounded) | 77.8 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-fish-unspecified-cooked-fish-wet-weight:37246c51f549
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) MeHg reference · 3 sampling families
Reference and scope
HMI Fish, species not stated (fish product) MeHg reference · 3 sampling families. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 26 | 91 | 110 |
| Alternative weighting | 26 | 91 | 110 |
8 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 33% |
| EFSA 2012 | 6 | 33% |
| Food 2011 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-fish-unspecified-fish-product-fish-wet-weight:a32be74c7f1e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) MeHg reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (fresh or raw) MeHg reference · 2 sampling families. Fish, wet weight; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 27–29.4 (bounded) | 50–97.5 (bounded) | 113 |
| Alternative weighting | 27–29.4 (bounded) | 50–97.5 (bounded) | 113 |
21 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 12 | 50% |
| EFSA 2012 | 9 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MeHg-fish-unspecified-fresh-fish-wet-weight:aff52c990692
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (cooked) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Tuna (cooked) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Tuna, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 75 | 97.5 | 168 |
| Alternative weighting | 75 | 97.5 | 168 |
16 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 16 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-tuna-cooked-fish-wet-weight:d2699b1a0d57
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Tuna (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 215 | 275 | 327 |
| Alternative weighting | 215 | 275 | 327 |
24 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 24 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-tuna-fresh-fish-wet-weight:da7ff71d002f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Swordfish (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Swordfish (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Swordfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 290 | 290 | 290 |
| Alternative weighting | 290 | 290 | 290 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-swordfish-fresh-fish-wet-weight:b1453f509ba1
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (cooked) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Mackerel (cooked) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Mackerel, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 52 | 70 | 105 |
| Alternative weighting | 52 | 70 | 105 |
9 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 9 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-mackerel-cooked-fish-wet-weight:d4f12d9cfff6
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Mackerel (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 65 | 165 | 300 |
| Alternative weighting | 65 | 165 | 300 |
21 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 21 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-mackerel-fresh-fish-wet-weight:e1bdc009f535
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Horse mackerel, jacks and trevally (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Horse mackerel, jacks and trevally (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, dry weight; Horse mackerel, jacks and trevally, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2360 | 2400 | 2440 |
| Alternative weighting | 2360 | 2400 | 2440 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-horse-mackerel-jack-fresh-fish-dry-weight:7bdf4dc2843c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Horse mackerel, jacks and trevally (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Horse mackerel, jacks and trevally (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Horse mackerel, jacks and trevally, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 590 | 600 | 610 |
| Alternative weighting | 590 | 600 | 610 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-horse-mackerel-jack-fresh-fish-wet-weight:7564568c43ad
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (cooked) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Herring (cooked) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Herring, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 50 | 50 | 60 |
| Alternative weighting | 50 | 50 | 60 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-herring-cooked-fish-wet-weight:b5257e200dde
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Herring (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Herring, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 39.5 | 55 | 70 |
| Alternative weighting | 39.5 | 55 | 70 |
15 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 15 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-herring-fresh-fish-wet-weight:40b2c2a5d043
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (cooked) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (cooked) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 50 | 50 | 50 |
| Alternative weighting | 50 | 50 | 50 |
5 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 5 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-sardine-pilchard-cooked-fish-wet-weight:b28fdf671aec
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 50 | 50 |
| Alternative weighting | 20 | 50 | 50 |
10 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 10 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-sardine-pilchard-fresh-fish-wet-weight:5f60ceae9070
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (cooked) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Salmon (cooked) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Salmon, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 24 | 35 | 42.1 |
| Alternative weighting | 24 | 35 | 42.1 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-salmon-cooked-fish-wet-weight:2a44eff9a4e7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Salmon (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Salmon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 24–30 (bounded) | 50 | 50 |
| Alternative weighting | 24–30 (bounded) | 50 | 50 |
18 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 18 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-salmon-fresh-fish-wet-weight:45d3f4f1f9d2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 50 | 150 |
| Alternative weighting | 10 | 50 | 150 |
22 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 22 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-trout-fresh-fish-wet-weight:c3076296b493
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (cooked) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Cod (cooked) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Cod, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 80 | 210 | 440 |
| Alternative weighting | 80 | 210 | 440 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-cod-cooked-fish-wet-weight:a41d18427d43
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Cod (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Cod, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 59.5 | 70 | 92 |
| Alternative weighting | 59.5 | 70 | 92 |
22 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 22 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-cod-fresh-fish-wet-weight:49a382b841f8
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Haddock (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Haddock (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Haddock, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 45.5 | 92 | 93.5 |
| Alternative weighting | 45.5 | 92 | 93.5 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-haddock-fresh-fish-wet-weight:85f7e7649037
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Pollock and saithe (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Pollock and saithe (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Pollock and saithe, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 104 | 104 | 104 |
| Alternative weighting | 104 | 104 | 104 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-pollock-saithe-fresh-fish-wet-weight:782d4929d87a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Barracuda (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Barracuda (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, dry weight; Barracuda, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 810 | 825 | 840 |
| Alternative weighting | 810 | 825 | 840 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-barracuda-fresh-fish-dry-weight:e2756118e62b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Barracuda (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Barracuda (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Barracuda, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 200 | 205 | 210 |
| Alternative weighting | 200 | 205 | 210 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-barracuda-fresh-fish-wet-weight:bfa50c5f2ae7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Catfish (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Catfish (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, dry weight; Catfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2220 | 2250 | 2280 |
| Alternative weighting | 2220 | 2250 | 2280 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-catfish-fresh-fish-dry-weight:afff9f55e9a4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Catfish (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Catfish (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Catfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 560 | 565 | 570 |
| Alternative weighting | 560 | 565 | 570 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-catfish-fresh-fish-wet-weight:77a4a4f15960
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (cooked) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (cooked) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Marine fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 360 | 545 | 653 |
| Alternative weighting | 360 | 545 | 653 |
8 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 8 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-fish-unspecified-marine-cooked-fish-wet-weight:45a9d6fd3f52
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 120 | 250 | 342 |
| Alternative weighting | 120 | 250 | 342 |
47 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 47 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-fish-unspecified-marine-fresh-fish-wet-weight:c5eb6f0d30fc
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (cooked) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (cooked) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Freshwater fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 90 | 145 | 270 |
| Alternative weighting | 90 | 145 | 270 |
8 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 8 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-fish-unspecified-freshwater-cooked-fish-wet-weight:1ae97d58ba36
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Freshwater fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 120 | 187 | 200 |
| Alternative weighting | 120 | 187 | 200 |
14 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 14 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-fish-unspecified-freshwater-fresh-fish-wet-weight:76f2652d4e77
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (cooked) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (cooked) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 33.4 | 44.5 | 51.5 |
| Alternative weighting | 33.4 | 44.5 | 51.5 |
6 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 6 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-fish-unspecified-cooked-fish-wet-weight:f7f373d2e4d8
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish product) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤6 | ≤14 | 14–70 (bounded) |
| Alternative weighting | ≤6 | ≤14 | 14–70 (bounded) |
5 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 5 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-fish-unspecified-fish-product-fish-wet-weight:be2472b1a9bf
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) Hg_unspecified reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fresh or raw) Hg_unspecified reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 15.5–30 (bounded) | 50 | 92–100 (bounded) |
| Alternative weighting | 15.5–30 (bounded) | 50 | 92–100 (bounded) |
36 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 36 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Hg_unspecified-fish-unspecified-fresh-fish-wet-weight:1a45971f26a5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (cooked) iHg reference · 1 sampling family
Reference and scope
HMI Tuna (cooked) iHg reference · 1 sampling family. Fish, wet weight; Tuna, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤10 | ≤10 |
| Alternative weighting | ≤10 | ≤10 | ≤10 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iHg-tuna-cooked-fish-wet-weight:a5c780bb73f2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) iHg reference · 1 sampling family
Reference and scope
HMI Tuna (fresh or raw) iHg reference · 1 sampling family. Fish, wet weight; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 180 | 307 | 700 |
| Alternative weighting | 180 | 307 | 700 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iHg-tuna-fresh-fish-wet-weight:3c5e3e74994b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) iHg reference · 1 sampling family
Reference and scope
HMI Mackerel (fresh or raw) iHg reference · 1 sampling family. Fish, wet weight; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 74 | 74 | 74 |
| Alternative weighting | 74 | 74 | 74 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iHg-mackerel-fresh-fish-wet-weight:c2ac677b400c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Horse mackerel, jacks and trevally (fresh or raw) iHg reference · 1 sampling family
Reference and scope
HMI Horse mackerel, jacks and trevally (fresh or raw) iHg reference · 1 sampling family. Fish, dry weight; Horse mackerel, jacks and trevally, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1070 | 1080 | 1080 |
| Alternative weighting | 1070 | 1080 | 1080 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iHg-horse-mackerel-jack-fresh-fish-dry-weight:2cb4373c289c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) iHg reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (fresh or raw) iHg reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 47–50 (bounded) | 47–50 (bounded) | 47–50 (bounded) |
| Alternative weighting | 47–50 (bounded) | 47–50 (bounded) | 47–50 (bounded) |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iHg-sardine-pilchard-fresh-fish-wet-weight:3852a0bd8b3f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) iHg reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) iHg reference · 1 sampling family. Fish, dry weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 30 | 30 |
| Alternative weighting | 30 | 30 | 30 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iHg-trout-fresh-fish-dry-weight:a111ce18c9f8
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) iHg reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) iHg reference · 1 sampling family. Fish, wet weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 22.3–23.3 (bounded) | 24.5–26.5 (bounded) |
| Alternative weighting | 20 | 22.3–23.3 (bounded) | 24.5–26.5 (bounded) |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iHg-trout-fresh-fish-wet-weight:0ed1f31c1d0a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fresh or raw) iHg reference · 1 sampling family
Reference and scope
HMI Cod (fresh or raw) iHg reference · 1 sampling family. Fish, wet weight; Cod, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 100 | 167 | 233 |
| Alternative weighting | 100 | 167 | 233 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iHg-cod-fresh-fish-wet-weight:9f192ce78cf2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Barracuda (fresh or raw) iHg reference · 1 sampling family
Reference and scope
HMI Barracuda (fresh or raw) iHg reference · 1 sampling family. Fish, dry weight; Barracuda, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 100 | 145 | 190 |
| Alternative weighting | 100 | 145 | 190 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iHg-barracuda-fresh-fish-dry-weight:545213eca82c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Catfish (fresh or raw) iHg reference · 1 sampling family
Reference and scope
HMI Catfish (fresh or raw) iHg reference · 1 sampling family. Fish, dry weight; Catfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 450 | 475 | 500 |
| Alternative weighting | 450 | 475 | 500 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| MERCURY SPECIATION IN… 2026 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iHg-catfish-fresh-fish-dry-weight:a88434ac3072
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (cooked) iHg reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (cooked) iHg reference · 1 sampling family. Fish, wet weight; Fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | 8.25–13.3 (bounded) | 16.5 |
| Alternative weighting | ≤10 | 8.25–13.3 (bounded) | 16.5 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iHg-fish-unspecified-cooked-fish-wet-weight:0f54b7bc4ddf
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) iHg reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (fish product) iHg reference · 2 sampling families. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 19.5 | 20 | 29.1 |
| Alternative weighting | 19.5 | 20 | 29.1 |
3 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 50% |
| Food 2011 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iHg-fish-unspecified-fish-product-fish-wet-weight:729ed5b54a69
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) iHg reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fresh or raw) iHg reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 40.3–47.3 (bounded) | 64.3–70 (bounded) | 215 |
| Alternative weighting | 40.3–47.3 (bounded) | 64.3–70 (bounded) | 215 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iHg-fish-unspecified-fresh-fish-wet-weight:3e696f99521c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (canned) Cd reference · 4 sampling families
Reference and scope
HMI Tuna (canned) Cd reference · 4 sampling families. Fish, wet weight; Tuna, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 3–3.31 (bounded) | 21 | 39.5 |
| Alternative weighting | 3–3.31 (bounded) | 21 | 39.5 |
15 reference units; 4 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 25% |
| Gladys et al. 2026 | 3 | 25% |
| De et al. 2021 | 8 | 25% |
| Olmedo et al. 2013 | 3 | 25% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-tuna-canned-fish-wet-weight:4bd93b9bd47b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (cooked) Cd reference · 1 sampling family
Reference and scope
HMI Tuna (cooked) Cd reference · 1 sampling family. Fish, wet weight; Tuna, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 11.8 | 15.5 | 23 |
| Alternative weighting | 11.8 | 15.5 | 23 |
6 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 6 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-tuna-cooked-fish-wet-weight:231ab9d691da
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) Cd reference · 2 sampling families
Reference and scope
HMI Tuna (fresh or raw) Cd reference · 2 sampling families. Fish, wet weight; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 8 | 8 | 12–13.5 (bounded) |
| Alternative weighting | 8 | 8 | 12–13.5 (bounded) |
36 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 35 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-tuna-fresh-fish-wet-weight:55e7e6f7dd77
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Tuna (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 15 | 18 | 22 |
| Alternative weighting | 15 | 18 | 22 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-tuna-fresh-fish-basis-not-stated:67009a0263aa
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Swordfish (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Swordfish (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Swordfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 35.9 | 35.9 | 35.9 |
| Alternative weighting | 35.9 | 35.9 | 35.9 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2009 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-swordfish-fresh-fish-basis-not-stated:58f5af32668c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Swordfish (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Swordfish (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Swordfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 9 | 9 | 9 |
| Alternative weighting | 9 | 9 | 9 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-swordfish-fresh-fish-wet-weight:1c9e5c730d0c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shark (fresh or raw) Cd reference · 3 sampling families
Reference and scope
HMI Shark (fresh or raw) Cd reference · 3 sampling families. Fish, wet weight; Shark, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤0.1 | ≤2 | 2–4 (bounded) |
| Alternative weighting | ≤0.1 | ≤2 | 2–4 (bounded) |
31 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 4 | 33% |
| Sang et al. 2019 | 25 | 33% |
| Olmedo et al. 2013 | 2 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-shark-fresh-fish-wet-weight:bf5c12d101c2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shark (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Shark (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Shark, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 20 | 20 |
| Alternative weighting | 20 | 20 | 20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-shark-fresh-fish-basis-not-stated:1abecbb6a584
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (canned) Cd reference · 1 sampling family
Reference and scope
HMI Mackerel (canned) Cd reference · 1 sampling family. Fish, wet weight; Mackerel, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 18 | 18 | 18 |
| Alternative weighting | 18 | 18 | 18 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-mackerel-canned-fish-wet-weight:b9e9c9b27557
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (cooked) Cd reference · 1 sampling family
Reference and scope
HMI Mackerel (cooked) Cd reference · 1 sampling family. Fish, wet weight; Mackerel, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10.9 | 10.9 | 10.9 |
| Alternative weighting | 10.9 | 10.9 | 10.9 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-mackerel-cooked-fish-wet-weight:dd0b2426de5b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) Cd reference · 2 sampling families
Reference and scope
HMI Mackerel (fresh or raw) Cd reference · 2 sampling families. Fish, wet weight; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1 | 1–1.5 (bounded) | 6.92–10 (bounded) |
| Alternative weighting | 1 | 1–1.5 (bounded) | 6.92–10 (bounded) |
21 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 20 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-mackerel-fresh-fish-wet-weight:da64b47ee16b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Mackerel (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 8 | 10 | 15 |
| Alternative weighting | 8 | 10 | 15 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-mackerel-fresh-fish-basis-not-stated:8e50396baa98
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Horse mackerel, jacks and trevally (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Horse mackerel, jacks and trevally (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Horse mackerel, jacks and trevally, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1 | 1 | 1 |
| Alternative weighting | 1 | 1 | 1 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-horse-mackerel-jack-fresh-fish-wet-weight:f1f1f921ce43
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (cooked) Cd reference · 1 sampling family
Reference and scope
HMI Herring (cooked) Cd reference · 1 sampling family. Fish, wet weight; Herring, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 12 | 12 | 12 |
| Alternative weighting | 12 | 12 | 12 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-herring-cooked-fish-wet-weight:2628061c9d20
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Herring (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Herring, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2.2 | 3–5 (bounded) | 6–7 (bounded) |
| Alternative weighting | ≤2.2 | 3–5 (bounded) | 6–7 (bounded) |
21 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 21 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-herring-fresh-fish-wet-weight:890dfcfb3351
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Herring (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Herring, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5 | 20 | 49 |
| Alternative weighting | 5 | 20 | 49 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-herring-fresh-fish-basis-not-stated:58461ed5c2c4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (canned) Cd reference · 2 sampling families
Reference and scope
HMI Sardine and pilchard (canned) Cd reference · 2 sampling families. Fish, wet weight; Sardine and pilchard, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤0.626 | 1–1.31 (bounded) | 8 |
| Alternative weighting | ≤0.626 | 1–1.31 (bounded) | 8 |
12 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| De et al. 2021 | 10 | 50% |
| Olmedo et al. 2013 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-sardine-pilchard-canned-fish-wet-weight:82d4a9509da7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (canned) Cd reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (canned) Cd reference · 1 sampling family. Fish, basis not stated; Sardine and pilchard, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 30 | 30 |
| Alternative weighting | 30 | 30 | 30 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Evaluation of… 2025 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-sardine-pilchard-canned-fish-basis-not-stated:3a4fd4b7533d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) Cd reference · 2 sampling families
Reference and scope
HMI Sardine and pilchard (fresh or raw) Cd reference · 2 sampling families. Fish, wet weight; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2 | 2 | 12–16 (bounded) |
| Alternative weighting | 2 | 2 | 12–16 (bounded) |
22 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 21 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-sardine-pilchard-fresh-fish-wet-weight:d7899888c68d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 21.5 | 33 | 65 |
| Alternative weighting | 21.5 | 33 | 65 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-sardine-pilchard-fresh-fish-basis-not-stated:5ea87a5eb76b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (canned) Cd reference · 1 sampling family
Reference and scope
HMI Anchovy (canned) Cd reference · 1 sampling family. Fish, wet weight; Anchovy, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 94 | 94 | 94 |
| Alternative weighting | 94 | 94 | 94 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-anchovy-canned-fish-wet-weight:dde0e26c7045
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Anchovy (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Anchovy, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1 | 1 | 1 |
| Alternative weighting | 1 | 1 | 1 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-anchovy-fresh-fish-wet-weight:875399f16e3c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Anchovy (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Anchovy, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 50 | 183 | 382 |
| Alternative weighting | 50 | 183 | 382 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-anchovy-fresh-fish-basis-not-stated:559145940dd6
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (canned) Cd reference · 1 sampling family
Reference and scope
HMI Salmon (canned) Cd reference · 1 sampling family. Fish, wet weight; Salmon, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤3 | ≤3 | ≤3 |
| Alternative weighting | ≤3 | ≤3 | ≤3 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-salmon-canned-fish-wet-weight:caefb83e59dd
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (cooked) Cd reference · 2 sampling families
Reference and scope
HMI Salmon (cooked) Cd reference · 2 sampling families. Fish, wet weight; Salmon, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1 | ≤1 | ≤2 |
| Alternative weighting | ≤1 | ≤1 | ≤2 |
19 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 18 | 50% |
| FDA TDS FY2018–FY2020 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-salmon-cooked-fish-wet-weight:bb2eb5ca9ec1
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Salmon (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Salmon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1 | ≤1.67 | ≤7.25 |
| Alternative weighting | ≤1 | ≤1.67 | ≤7.25 |
7 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 7 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-salmon-fresh-fish-wet-weight:3ae091916ab3
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Salmon (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Salmon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5 | 10 | 20 |
| Alternative weighting | 5 | 10 | 20 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-salmon-fresh-fish-basis-not-stated:ce6c225e4076
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) Cd reference · 1 sampling family. Fish, dry weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2 | ≤2 | ≤2 |
| Alternative weighting | ≤2 | ≤2 | ≤2 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-trout-fresh-fish-dry-weight:82855f42a50c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2 | ≤2.7 | ≤4 |
| Alternative weighting | ≤2 | ≤2.7 | ≤4 |
20 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 20 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-trout-fresh-fish-wet-weight:2c6ee2d9b649
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 20 | 20 |
| Alternative weighting | 20 | 20 | 20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-trout-fresh-fish-basis-not-stated:f728869beb0b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (cooked) Cd reference · 2 sampling families
Reference and scope
HMI Cod (cooked) Cd reference · 2 sampling families. Fish, wet weight; Cod, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1 | 0.6–1.1 (bounded) | 1.2 |
| Alternative weighting | ≤1 | 0.6–1.1 (bounded) | 1.2 |
2 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 50% |
| FDA TDS FY2018–FY2020 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-cod-cooked-fish-wet-weight:4b391016740e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fish oil) Cd reference · 1 sampling family
Reference and scope
HMI Cod (fish oil) Cd reference · 1 sampling family. Fish, wet weight; Cod, fish oil; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤4.6 | ≤5 | ≤8 |
| Alternative weighting | ≤4.6 | ≤5 | ≤8 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-cod-fish-oil-fish-wet-weight:a3a17296f6f6
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fresh or raw) Cd reference · 2 sampling families
Reference and scope
HMI Cod (fresh or raw) Cd reference · 2 sampling families. Fish, wet weight; Cod, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2 | 2 | 2–3.3 (bounded) |
| Alternative weighting | ≤2 | 2 | 2–3.3 (bounded) |
21 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 20 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-cod-fresh-fish-wet-weight:88399604e42c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Cod (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Cod, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5 | 5 | 5 |
| Alternative weighting | 5 | 5 | 5 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-cod-fresh-fish-basis-not-stated:bcadfc3c9ab2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Haddock (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Haddock (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Haddock, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1.6 | 4.7–5.5 (bounded) | 9.4 |
| Alternative weighting | ≤1.6 | 4.7–5.5 (bounded) | 9.4 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-haddock-fresh-fish-wet-weight:11abb3eb4eaf
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Haddock (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Haddock (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Haddock, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5 | 5 | 30 |
| Alternative weighting | 5 | 5 | 30 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-haddock-fresh-fish-basis-not-stated:82df02ba9863
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Pollock and saithe (cooked) Cd reference · 1 sampling family
Reference and scope
HMI Pollock and saithe (cooked) Cd reference · 1 sampling family. Fish, wet weight; Pollock and saithe, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 9 | 9 | 11.5 |
| Alternative weighting | 9 | 9 | 11.5 |
15 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 15 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-pollock-saithe-cooked-fish-wet-weight:b0f87f7f5706
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Pollock and saithe (fish product) Cd reference · 1 sampling family
Reference and scope
HMI Pollock and saithe (fish product) Cd reference · 1 sampling family. Fish, wet weight; Pollock and saithe, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 4 | 5 | 6 |
| Alternative weighting | 4 | 5 | 6 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Naess et al. 2020 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-pollock-saithe-fish-product-fish-wet-weight:816ae591e840
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Pollock and saithe (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Pollock and saithe (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Pollock and saithe, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 9.6 | 9.6 | 9.6 |
| Alternative weighting | 9.6 | 9.6 | 9.6 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-pollock-saithe-fresh-fish-wet-weight:031a1c5cf276
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Whiting and blue whiting (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Whiting and blue whiting (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Whiting and blue whiting, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5 | 5 | 5 |
| Alternative weighting | 5 | 5 | 5 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-whiting-blue-whiting-fresh-fish-basis-not-stated:4215f43e80c0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hake (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Hake (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Hake, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1 | 4 | 7 |
| Alternative weighting | 1 | 4 | 7 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-hake-fresh-fish-wet-weight:c50d46d2e5b2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hake (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Hake (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Hake, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5 | 5 | 5 |
| Alternative weighting | 5 | 5 | 5 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-hake-fresh-fish-basis-not-stated:aa45404d2392
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (cooked) Cd reference · 1 sampling family
Reference and scope
HMI Plaice, flounder, sole and turbot (cooked) Cd reference · 1 sampling family. Fish, wet weight; Plaice, flounder, sole and turbot, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2 | ≤2 | ≤2 |
| Alternative weighting | ≤2 | ≤2 | ≤2 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-plaice-flounder-sole-cooked-fish-wet-weight:14e618e636cb
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (fresh or raw) Cd reference · 2 sampling families
Reference and scope
HMI Plaice, flounder, sole and turbot (fresh or raw) Cd reference · 2 sampling families. Fish, wet weight; Plaice, flounder, sole and turbot, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1 | 1 | 3 |
| Alternative weighting | 0.2–1 (bounded) | 1 | 3 |
7 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 5 | 50% |
| Olmedo et al. 2013 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-plaice-flounder-sole-fresh-fish-wet-weight:9f4854d816c3
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Plaice, flounder, sole and turbot (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Plaice, flounder, sole and turbot, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5 | 5 | 5 |
| Alternative weighting | 5 | 5 | 5 |
5 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 5 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-plaice-flounder-sole-fresh-fish-basis-not-stated:8050fae1dd78
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bass and barramundi (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Sea bass and barramundi (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Sea bass and barramundi, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 13 | 13 | 13 |
| Alternative weighting | 13 | 13 | 13 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-sea-bass-fresh-fish-basis-not-stated:e00d67a1fb04
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bass and barramundi (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Sea bass and barramundi (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Sea bass and barramundi, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2 | 2 | 2 |
| Alternative weighting | 2 | 2 | 2 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-sea-bass-fresh-fish-wet-weight:2b4e7c001cb4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bream and porgies (fresh or raw) Cd reference · 2 sampling families
Reference and scope
HMI Sea bream and porgies (fresh or raw) Cd reference · 2 sampling families. Fish, wet weight; Sea bream and porgies, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1 | 1 | 1 |
| Alternative weighting | 1 | 1 | 1 |
4 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 3 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-sea-bream-porgy-fresh-fish-wet-weight:1561adb1e585
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bream and porgies (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Sea bream and porgies (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Sea bream and porgies, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 8 | 36 | 64 |
| Alternative weighting | 8 | 36 | 64 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-sea-bream-porgy-fresh-fish-basis-not-stated:05c5fe2519f2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Grey mullet (fresh or raw) Cd reference · 2 sampling families
Reference and scope
HMI Grey mullet (fresh or raw) Cd reference · 2 sampling families. Fish, basis not stated; Grey mullet, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 23.8 | 36.9 | 50 |
| Alternative weighting | 23.8 | 36.9 | 50 |
2 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Bakhshalizadeh et al. 2023 | 1 | 50% |
| European et al. 2004 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-grey-mullet-fresh-fish-basis-not-stated:b0b5a8558558
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Grey mullet (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Grey mullet (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Grey mullet, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 12.8 | 12.8 | 12.8 |
| Alternative weighting | 12.8 | 12.8 | 12.8 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Cirillo et al. 2010 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-grey-mullet-fresh-fish-wet-weight:e80ea03877e0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Barracuda (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Barracuda (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Barracuda, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 6 | 6 | 6 |
| Alternative weighting | 6 | 6 | 6 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-barracuda-fresh-fish-wet-weight:4fc396957129
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anglerfish and monkfish (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Anglerfish and monkfish (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Anglerfish and monkfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1 | 1 | 1 |
| Alternative weighting | 1 | 1 | 1 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-anglerfish-monkfish-fresh-fish-wet-weight:c0377d52ebd9
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Gurnard (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Gurnard (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Gurnard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 0.4 | 0.4 | 0.4 |
| Alternative weighting | 0.4 | 0.4 | 0.4 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-gurnard-fresh-fish-wet-weight:19544b15e771
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Gurnard (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Gurnard (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Gurnard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5 | 5 | 5 |
| Alternative weighting | 5 | 5 | 5 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-gurnard-fresh-fish-basis-not-stated:bf80378a1356
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Eel (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Eel (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Eel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1 | ≤1 | ≤1 |
| Alternative weighting | ≤1 | ≤1 | ≤1 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-eel-fresh-fish-wet-weight:acf73bf1c6f9
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Eel (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Eel (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Eel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5 | 5 | 5 |
| Alternative weighting | 5 | 5 | 5 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-eel-fresh-fish-basis-not-stated:2b3a3acd51a4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tilapia (cooked) Cd reference · 1 sampling family
Reference and scope
HMI Tilapia (cooked) Cd reference · 1 sampling family. Fish, wet weight; Tilapia, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1 | ≤1 | ≤1 |
| Alternative weighting | ≤1 | ≤1 | ≤1 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-tilapia-cooked-fish-wet-weight:fb9b99f25516
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (cooked) Cd reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (cooked) Cd reference · 1 sampling family. Fish, wet weight; Carp and other cyprinids, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2 | ≤2 | ≤2 |
| Alternative weighting | ≤2 | ≤2 | ≤2 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-carp-cyprinid-cooked-fish-wet-weight:12a154b6f9f0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (cooked) Cd reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (cooked) Cd reference · 1 sampling family. Fish, basis not stated; Carp and other cyprinids, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 4 | 4 | 4 |
| Alternative weighting | 4 | 4 | 4 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Venant et al. 2025 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-carp-cyprinid-cooked-fish-basis-not-stated:d0c20fc130ca
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (fresh or raw) Cd reference · 2 sampling families
Reference and scope
HMI Carp and other cyprinids (fresh or raw) Cd reference · 2 sampling families. Fish, wet weight; Carp and other cyprinids, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 3 | 7 | 10 |
| Alternative weighting | 3 | 7 | 10 |
4 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 50% |
| Venant et al. 2025 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-carp-cyprinid-fresh-fish-wet-weight:21df1431172c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (fresh or raw) Cd reference · 2 sampling families
Reference and scope
HMI Carp and other cyprinids (fresh or raw) Cd reference · 2 sampling families. Fish, basis not stated; Carp and other cyprinids, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 12 | 73.5 | 130 |
| Alternative weighting | 12 | 73.5 | 130 |
11 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Subhanullah et al. 2024 | 1 | 50% |
| Venant et al. 2025 | 10 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-carp-cyprinid-fresh-fish-basis-not-stated:3ea3640c27cc
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (fresh or raw) Cd reference · 1 sampling family. Fish, dry weight; Carp and other cyprinids, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 31 | 31 | 31 |
| Alternative weighting | 31 | 31 | 31 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Venant et al. 2025 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-carp-cyprinid-fresh-fish-dry-weight:b96a03a25b17
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (smoked, dried, salted or fermented) Cd reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (smoked, dried, salted or fermented) Cd reference · 1 sampling family. Fish, basis not stated; Carp and other cyprinids, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 13 | 13.5 | 17 |
| Alternative weighting | 13 | 13.5 | 17 |
6 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Venant et al. 2025 | 6 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-carp-cyprinid-smoked-dried-salted-fermented-fish-basis-not-stated:9823ffe4c89c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Catfish (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Catfish (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Catfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2 | 2 | 2 |
| Alternative weighting | 2 | 2 | 2 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-catfish-fresh-fish-wet-weight:c4ce5c8200ca
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Perch, walleye and zander (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Perch, walleye and zander (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Perch, walleye and zander, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2 | ≤2 | ≤2 |
| Alternative weighting | ≤2 | ≤2 | ≤2 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-perch-walleye-fresh-fish-wet-weight:7905328e66f0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other freshwater fish (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Other freshwater fish (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Other freshwater fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2 | 2 | 2 |
| Alternative weighting | 2 | 2 | 2 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-other-freshwater-finfish-fresh-fish-wet-weight:0e8798980681
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Bream (species group not stated) (cooked) Cd reference · 1 sampling family
Reference and scope
HMI Bream (species group not stated) (cooked) Cd reference · 1 sampling family. Fish, wet weight; Bream (species group not stated), cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 7.5 | 7.5 | 7.5 |
| Alternative weighting | 7.5 | 7.5 | 7.5 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-bream-unspecified-cooked-fish-wet-weight:5219d65009bb
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Bream (species group not stated) (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Bream (species group not stated) (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Bream (species group not stated), fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2 | 1–2.5 (bounded) | 2–3 (bounded) |
| Alternative weighting | ≤2 | 1–2.5 (bounded) | 2–3 (bounded) |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-bream-unspecified-fresh-fish-wet-weight:a33d19aae386
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (cooked) Cd reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (cooked) Cd reference · 1 sampling family. Fish, wet weight; Marine fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 15 | 15 | 15 |
| Alternative weighting | 15 | 15 | 15 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-marine-cooked-fish-wet-weight:fadfbfae55df
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (cooked) Cd reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (cooked) Cd reference · 1 sampling family. Fish, basis not stated; Marine fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2.71 | 2.71 | 2.71 |
| Alternative weighting | 2.71 | 2.71 | 2.71 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Dabeka et al. 1995 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-marine-cooked-fish-basis-not-stated:a28ea9a2dae4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1.2 | 1.2 | 2.9 |
| Alternative weighting | 1.2 | 1.2 | 2.9 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Cirillo et al. 2010 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-marine-fresh-fish-wet-weight:309a50cc30ef
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) Cd reference · 2 sampling families
Reference and scope
HMI Marine fish, species not stated (fresh or raw) Cd reference · 2 sampling families. Fish, basis not stated; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1.64 | 3.32 | 5 |
| Alternative weighting | 1.64 | 3.32 | 5 |
2 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Dabeka et al. 1995 | 1 | 50% |
| European et al. 2004 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-marine-fresh-fish-basis-not-stated:f4c87cab17bc
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (cooked) Cd reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (cooked) Cd reference · 1 sampling family. Fish, wet weight; Freshwater fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤0.3 | ≤0.3 | ≤0.3 |
| Alternative weighting | ≤0.3 | ≤0.3 | ≤0.3 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-freshwater-cooked-fish-wet-weight:b7435ebef698
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (cooked) Cd reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (cooked) Cd reference · 1 sampling family. Fish, basis not stated; Freshwater fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2.37 | 2.37 | 2.37 |
| Alternative weighting | 2.37 | 2.37 | 2.37 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Dabeka et al. 1995 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-freshwater-cooked-fish-basis-not-stated:e82365d420f1
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (fresh or raw) Cd reference · 1 sampling family. Fish, basis not stated; Freshwater fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1.11 | 1.11 | 1.11 |
| Alternative weighting | 1.11 | 1.11 | 1.11 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Dabeka et al. 1995 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-freshwater-fresh-fish-basis-not-stated:7853a1cb588f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) Cd reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (canned) Cd reference · 2 sampling families. Fish, wet weight; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 19 | 19 | 19 |
| Alternative weighting | 19 | 19 | 19 |
4 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 50% |
| Baxter et al. 2015 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-canned-fish-wet-weight:d7829d546620
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) Cd reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (canned) Cd reference · 1 sampling family. Fish, basis not stated; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 9.25 | 9.25 | 9.25 |
| Alternative weighting | 9.25 | 9.25 | 9.25 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Dabeka et al. 1995 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-canned-fish-basis-not-stated:b0159b885b24
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (cooked) Cd reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (cooked) Cd reference · 2 sampling families. Fish, wet weight; Fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2.02 | ≤3 | ≤3 |
| Alternative weighting | ≤2.02 | ≤3 | ≤3 |
34 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 32 | 50% |
| Baxter et al. 2015 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-cooked-fish-wet-weight:6d4c87aea4e2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish oil) Cd reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish oil) Cd reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fish oil; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤18.3 | ≤30 |
| Alternative weighting | ≤10 | ≤18.3 | ≤30 |
10 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 10 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-fish-oil-fish-wet-weight:57410e427048
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) Cd reference · 3 sampling families
Reference and scope
HMI Fish, species not stated (fish product) Cd reference · 3 sampling families. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5.5–6.38 (bounded) | 7–10 (bounded) | 12 |
| Alternative weighting | 6–6.5 (bounded) | 7–10 (bounded) | 12 |
35 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 32 | 33% |
| FDA TDS FY2018–FY2020 | 1 | 33% |
| Baxter et al. 2015 | 2 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-fish-product-fish-wet-weight:bffaf7b415d5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) Cd reference · 3 sampling families
Reference and scope
HMI Fish, species not stated (fish product) Cd reference · 3 sampling families. Fish, basis not stated; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 12 | 22 | 26 |
| Alternative weighting | 12 | 22 | 26 |
5 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 33% |
| EFSA 2009 | 1 | 33% |
| European et al. 2004 | 3 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-fish-product-fish-basis-not-stated:12a6b642ae06
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish sauce) Cd reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish sauce) Cd reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fish sauce; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | 1550–1560 (bounded) | 3100 |
| Alternative weighting | ≤10 | 1550–1560 (bounded) | 3100 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-fish-sauce-fish-wet-weight:4182037785e4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish sauce) Cd reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish sauce) Cd reference · 1 sampling family. Fish, basis not stated; Fish, species not stated, fish sauce; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 27500 | 32000 | 36600 |
| Alternative weighting | 27500 | 32000 | 36600 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Abdullah 2009 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-fish-sauce-fish-basis-not-stated:ba1032636977
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fresh or raw) Cd reference · 1 sampling family. Fish, dry weight; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 330 | 330 | 330 |
| Alternative weighting | 330 | 330 | 330 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-fresh-fish-dry-weight:3ca5efbbbcfc
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) Cd reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fresh or raw) Cd reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2.1 | ≤3.2 | 2.67–5 (bounded) |
| Alternative weighting | ≤2.05 | ≤3.15 | 2.74–5 (bounded) |
49 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 49 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-fresh-fish-wet-weight:9a8740c98401
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) Cd reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (fresh or raw) Cd reference · 2 sampling families. Fish, basis not stated; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5 | 12.5 | 25 |
| Alternative weighting | 5 | 12.5 | 25 |
5 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| EFSA 2009 | 2 | 50% |
| European et al. 2004 | 3 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-fresh-fish-basis-not-stated:16efc0ed57ba
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (smoked, dried, salted or fermented) Cd reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (smoked, dried, salted or fermented) Cd reference · 1 sampling family. Fish, dry weight; Fish, species not stated, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 280 | 330 | 380 |
| Alternative weighting | 280 | 330 | 380 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-smoked-dried-salted-fermented-fish-dry-weight:fa7f39765ce0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (smoked, dried, salted or fermented) Cd reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (smoked, dried, salted or fermented) Cd reference · 1 sampling family. Fish, wet weight; Fish, species not stated, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2.8 | 30.7 | 204 |
| Alternative weighting | ≤2.8 | 27.4 | 112 |
8 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 8 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-smoked-dried-salted-fermented-fish-wet-weight:346e4a720bae
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (smoked, dried, salted or fermented) Cd reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (smoked, dried, salted or fermented) Cd reference · 2 sampling families. Fish, basis not stated; Fish, species not stated, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 70 | 75 | 90 |
| Alternative weighting | 70 | 75 | 90 |
6 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 50% |
| Bazie et al. 2022 | 5 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cd-fish-unspecified-smoked-dried-salted-fermented-fish-basis-not-stated:bfe4b1a8e9e3
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (canned) Pb reference · 4 sampling families
Reference and scope
HMI Tuna (canned) Pb reference · 4 sampling families. Fish, wet weight; Tuna, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤4.55 | 115–117 (bounded) | 289 |
| Alternative weighting | ≤4.55 | 115–117 (bounded) | 289 |
14 reference units; 4 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 25% |
| Gladys et al. 2026 | 3 | 25% |
| De et al. 2021 | 8 | 25% |
| Rodriguez-Mendivil et al. 2019 | 2 | 25% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-tuna-canned-fish-wet-weight:a32aeeb54a78
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Tuna (cooked) Pb reference · 1 sampling family. Fish, wet weight; Tuna, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤5 | ≤10 | 5–10 (bounded) |
| Alternative weighting | ≤5 | ≤10 | 5–10 (bounded) |
14 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 14 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-tuna-cooked-fish-wet-weight:f3fc396119d6
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Tuna (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤10 | ≤18.9 |
| Alternative weighting | ≤10 | ≤10 | ≤18.9 |
47 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 47 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-tuna-fresh-fish-wet-weight:ae12e50833b7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shark (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Shark (fresh or raw) Pb reference · 1 sampling family. Fish, basis not stated; Shark, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | 55–60 (bounded) | 110 |
| Alternative weighting | ≤10 | 55–60 (bounded) | 110 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-shark-fresh-fish-basis-not-stated:adf04a4b759a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shark (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Shark (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Shark, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 6.3 | 23.1 | 60 |
| Alternative weighting | 6.3 | 23.1 | 60 |
25 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Sang et al. 2019 | 25 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-shark-fresh-fish-wet-weight:e24258a98316
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Mackerel (cooked) Pb reference · 1 sampling family. Fish, wet weight; Mackerel, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤10 | 27–29.5 (bounded) |
| Alternative weighting | ≤10 | ≤10 | 27–29.5 (bounded) |
10 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 10 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-mackerel-cooked-fish-wet-weight:67c4b5fd765a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Mackerel (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤7 | ≤10 | 1–20 (bounded) |
| Alternative weighting | ≤7 | ≤10 | 1–20 (bounded) |
41 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 41 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-mackerel-fresh-fish-wet-weight:cfd42f1d8baf
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Herring (cooked) Pb reference · 1 sampling family. Fish, wet weight; Herring, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 49 | 49 | 49 |
| Alternative weighting | 49 | 49 | 49 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-herring-cooked-fish-wet-weight:65edc7650c92
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Herring (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Herring, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1 | ≤10 | 5.17–18 (bounded) |
| Alternative weighting | ≤1 | ≤10 | 5.17–18 (bounded) |
30 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 30 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-herring-fresh-fish-wet-weight:cc8bef99152b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (canned) Pb reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (canned) Pb reference · 1 sampling family. Fish, basis not stated; Sardine and pilchard, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 150 | 150 | 150 |
| Alternative weighting | 150 | 150 | 150 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Evaluation of… 2025 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-sardine-pilchard-canned-fish-basis-not-stated:b8d5483cabdd
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (canned) Pb reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (canned) Pb reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤5.1 | ≤5.1 | 7 |
| Alternative weighting | ≤5.1 | ≤5.1 | 7 |
10 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| De et al. 2021 | 10 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-sardine-pilchard-canned-fish-wet-weight:b9873c8ee662
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (cooked) Pb reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤10 | 2.5–10 (bounded) |
| Alternative weighting | ≤10 | ≤10 | 2.5–10 (bounded) |
9 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 9 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-sardine-pilchard-cooked-fish-wet-weight:b696042139c0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤19 | 12–38 (bounded) |
| Alternative weighting | ≤10 | ≤19 | 12–38 (bounded) |
34 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 34 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-sardine-pilchard-fresh-fish-wet-weight:d9cda715b9a1
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (canned) Pb reference · 1 sampling family
Reference and scope
HMI Anchovy (canned) Pb reference · 1 sampling family. Fish, wet weight; Anchovy, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 77 | 77 | 77 |
| Alternative weighting | 77 | 77 | 77 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-anchovy-canned-fish-wet-weight:4fdd06213cd5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (canned) Pb reference · 1 sampling family
Reference and scope
HMI Salmon (canned) Pb reference · 1 sampling family. Fish, wet weight; Salmon, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2 | ≤2 | ≤2 |
| Alternative weighting | ≤2 | ≤2 | ≤2 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-salmon-canned-fish-wet-weight:595549b86ab7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (cooked) Pb reference · 2 sampling families
Reference and scope
HMI Salmon (cooked) Pb reference · 2 sampling families. Fish, wet weight; Salmon, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤4 | ≤4 | ≤10 |
| Alternative weighting | ≤4 | ≤4 | ≤10 |
28 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 27 | 50% |
| FDA TDS FY2018–FY2020 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-salmon-cooked-fish-wet-weight:5b712c90a482
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Salmon (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Salmon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1 | ≤10 | ≤12 |
| Alternative weighting | ≤1 | ≤10 | ≤12 |
19 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 19 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-salmon-fresh-fish-wet-weight:31caeb7f8da5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) Pb reference · 1 sampling family. Fish, dry weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤20 | ≤20 |
| Alternative weighting | ≤20 | ≤20 | ≤20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-trout-fresh-fish-dry-weight:beace7c088af
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤9 | ≤11.1 | ≤17.8 |
| Alternative weighting | ≤9 | ≤11.1 | ≤17.8 |
28 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 28 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-trout-fresh-fish-wet-weight:2bbc049de549
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Cod (cooked) Pb reference · 1 sampling family. Fish, wet weight; Cod, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤4 | ≤4 | ≤4 |
| Alternative weighting | ≤4 | ≤4 | ≤4 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-cod-cooked-fish-wet-weight:a595073ea41b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fish oil) Pb reference · 1 sampling family
Reference and scope
HMI Cod (fish oil) Pb reference · 1 sampling family. Fish, wet weight; Cod, fish oil; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤25 | 4–60 (bounded) |
| Alternative weighting | ≤20 | ≤25 | 4–60 (bounded) |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-cod-fish-oil-fish-wet-weight:7408949056c9
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Cod (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Cod, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤5.83 | ≤10 | ≤15 |
| Alternative weighting | ≤5.83 | ≤10 | ≤15 |
29 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 29 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-cod-fresh-fish-wet-weight:79adf89d1399
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Haddock (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Haddock (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Haddock, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤5 | ≤5 | ≤5 |
| Alternative weighting | ≤5 | ≤5 | ≤5 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-haddock-fresh-fish-wet-weight:a9399730f2c8
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Pollock and saithe (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Pollock and saithe (cooked) Pb reference · 1 sampling family. Fish, wet weight; Pollock and saithe, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤10 | ≤10 |
| Alternative weighting | ≤10 | ≤10 | ≤10 |
15 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 15 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-pollock-saithe-cooked-fish-wet-weight:92bf414e2e49
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Pollock and saithe (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Pollock and saithe (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Pollock and saithe, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤5 | ≤5 | ≤5 |
| Alternative weighting | ≤5 | ≤5 | ≤5 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-pollock-saithe-fresh-fish-wet-weight:f6c7f48d99ae
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hake (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Hake (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Hake, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 86 | 90 | 94 |
| Alternative weighting | 86 | 90 | 94 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-hake-fresh-fish-wet-weight:8d8a57033964
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Plaice, flounder, sole and turbot (cooked) Pb reference · 1 sampling family. Fish, wet weight; Plaice, flounder, sole and turbot, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 4 | 5 | 6 |
| Alternative weighting | 4 | 5 | 6 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-plaice-flounder-sole-cooked-fish-wet-weight:2504d32bddb6
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (fresh or raw) Pb reference · 2 sampling families
Reference and scope
HMI Plaice, flounder, sole and turbot (fresh or raw) Pb reference · 2 sampling families. Fish, wet weight; Plaice, flounder, sole and turbot, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤12 | 26–32 (bounded) | 298 |
| Alternative weighting | ≤12 | 26–32 (bounded) | 298 |
5 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 50% |
| Olmedo et al. 2013 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-plaice-flounder-sole-fresh-fish-wet-weight:9846e7e5f225
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bream and porgies (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Sea bream and porgies (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Sea bream and porgies, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 20 | 170 |
| Alternative weighting | 10 | 20 | 170 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-sea-bream-porgy-fresh-fish-wet-weight:e664dbb35bbd
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bream and porgies (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Sea bream and porgies (fresh or raw) Pb reference · 1 sampling family. Fish, basis not stated; Sea bream and porgies, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 40 | 93.5 | 147 |
| Alternative weighting | 40 | 93.5 | 147 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-sea-bream-porgy-fresh-fish-basis-not-stated:fc57b3bc3c68
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Grey mullet (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Grey mullet (fresh or raw) Pb reference · 1 sampling family. Fish, basis not stated; Grey mullet, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 67.2 | 67.2 | 67.2 |
| Alternative weighting | 67.2 | 67.2 | 67.2 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Bakhshalizadeh et al. 2023 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-grey-mullet-fresh-fish-basis-not-stated:65ee7ec66caa
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Barracuda (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Barracuda (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Barracuda, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1 | 1 | 1 |
| Alternative weighting | 1 | 1 | 1 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-barracuda-fresh-fish-wet-weight:0b0a15ad3616
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Gurnard (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Gurnard (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Gurnard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 10 |
| Alternative weighting | 10 | 10 | 10 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-gurnard-fresh-fish-wet-weight:02e732640017
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tilapia (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Tilapia (cooked) Pb reference · 1 sampling family. Fish, wet weight; Tilapia, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤4 | ≤4 | ≤4 |
| Alternative weighting | ≤4 | ≤4 | ≤4 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-tilapia-cooked-fish-wet-weight:81190ac14a11
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (cooked) Pb reference · 1 sampling family. Fish, wet weight; Carp and other cyprinids, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5 | 7 | 9 |
| Alternative weighting | 5 | 7 | 9 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-carp-cyprinid-cooked-fish-wet-weight:62d9835a72a1
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (cooked) Pb reference · 1 sampling family. Fish, basis not stated; Carp and other cyprinids, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 85 | 85 | 85 |
| Alternative weighting | 85 | 85 | 85 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Venant et al. 2025 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-carp-cyprinid-cooked-fish-basis-not-stated:e413ab1be953
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (fresh or raw) Pb reference · 3 sampling families
Reference and scope
HMI Carp and other cyprinids (fresh or raw) Pb reference · 3 sampling families. Fish, basis not stated; Carp and other cyprinids, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 88 | 478 | 2080 |
| Alternative weighting | 88 | 478 | 2080 |
21 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Najem et al. 2024 | 10 | 33% |
| Subhanullah et al. 2024 | 1 | 33% |
| Venant et al. 2025 | 10 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-carp-cyprinid-fresh-fish-basis-not-stated:6a41842a1ba3
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Carp and other cyprinids, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 65 | 65 | 65 |
| Alternative weighting | 65 | 65 | 65 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Venant et al. 2025 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-carp-cyprinid-fresh-fish-wet-weight:059c116ab01b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (fresh or raw) Pb reference · 1 sampling family. Fish, dry weight; Carp and other cyprinids, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 203 | 203 | 203 |
| Alternative weighting | 203 | 203 | 203 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Venant et al. 2025 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-carp-cyprinid-fresh-fish-dry-weight:9c5a3dc4a577
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (smoked, dried, salted or fermented) Pb reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (smoked, dried, salted or fermented) Pb reference · 1 sampling family. Fish, basis not stated; Carp and other cyprinids, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 92 | 97 | 100 |
| Alternative weighting | 92 | 97 | 100 |
5 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Venant et al. 2025 | 5 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-carp-cyprinid-smoked-dried-salted-fermented-fish-basis-not-stated:1f38318817d6
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Perch, walleye and zander (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Perch, walleye and zander (fresh or raw) Pb reference · 1 sampling family. Fish, basis not stated; Perch, walleye and zander, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 183 | 183 | 183 |
| Alternative weighting | 183 | 183 | 183 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-perch-walleye-fresh-fish-basis-not-stated:e631b074dd86
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Bream (species group not stated) (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Bream (species group not stated) (cooked) Pb reference · 1 sampling family. Fish, wet weight; Bream (species group not stated), cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 14.5 | 14.5 | 14.5 |
| Alternative weighting | 14.5 | 14.5 | 14.5 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-bream-unspecified-cooked-fish-wet-weight:74007fd4bcd6
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (cooked) Pb reference · 1 sampling family. Fish, wet weight; Marine fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 3.75 | 5.13–5.45 (bounded) | 6.5–7.15 (bounded) |
| Alternative weighting | 3.75 | 5.13–5.45 (bounded) | 6.5–7.15 (bounded) |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-marine-cooked-fish-wet-weight:b78f51bb857f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (cooked) Pb reference · 1 sampling family. Fish, basis not stated; Marine fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 12 | 12 | 12 |
| Alternative weighting | 12 | 12 | 12 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Dabeka et al. 1995 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-marine-cooked-fish-basis-not-stated:5e71a48ab6e4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fish product) Pb reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (fish product) Pb reference · 1 sampling family. Fish, wet weight; Marine fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 6 | 6 | 6 |
| Alternative weighting | 6 | 6 | 6 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Naess et al. 2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-marine-fish-product-fish-wet-weight:a5ff2f98a19d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) Pb reference · 2 sampling families
Reference and scope
HMI Marine fish, species not stated (fresh or raw) Pb reference · 2 sampling families. Fish, wet weight; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2.33–3.1 (bounded) | 23 | 50 |
| Alternative weighting | 2.33–3.1 (bounded) | 23 | 50 |
23 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 20 | 50% |
| Cirillo et al. 2010 | 3 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-marine-fresh-fish-wet-weight:807351b73130
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (fresh or raw) Pb reference · 1 sampling family. Fish, dry weight; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 6 | 6 | 6 |
| Alternative weighting | 6 | 6 | 6 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-marine-fresh-fish-dry-weight:2f7c5f0b5da5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (fresh or raw) Pb reference · 1 sampling family. Fish, basis not stated; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 8.9 | 8.9 | 8.9 |
| Alternative weighting | 8.9 | 8.9 | 8.9 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Dabeka et al. 1995 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-marine-fresh-fish-basis-not-stated:462da875a020
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (cooked) Pb reference · 1 sampling family. Fish, wet weight; Freshwater fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤10 | ≤10 |
| Alternative weighting | ≤10 | ≤10 | ≤10 |
13 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 13 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-freshwater-cooked-fish-wet-weight:f48b06997cb7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (cooked) Pb reference · 1 sampling family. Fish, basis not stated; Freshwater fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 9.9 | 9.9 | 9.9 |
| Alternative weighting | 9.9 | 9.9 | 9.9 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Dabeka et al. 1995 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-freshwater-cooked-fish-basis-not-stated:4027488070a7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (fresh or raw) Pb reference · 1 sampling family. Fish, dry weight; Freshwater fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 3 | 3 | 3 |
| Alternative weighting | 3 | 3 | 3 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-freshwater-fresh-fish-dry-weight:4611bb6b47be
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Freshwater fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤3 | 0.5–10 (bounded) | 10–12 (bounded) |
| Alternative weighting | ≤3 | 0.5–10 (bounded) | 10–12 (bounded) |
22 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 22 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-freshwater-fresh-fish-wet-weight:1f12489bfd4b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (fresh or raw) Pb reference · 2 sampling families
Reference and scope
HMI Freshwater fish, species not stated (fresh or raw) Pb reference · 2 sampling families. Fish, basis not stated; Freshwater fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | 8.15–14.3 (bounded) | 14.3 |
| Alternative weighting | ≤10 | 8.15–14.3 (bounded) | 14.3 |
10 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 9 | 50% |
| Dabeka et al. 1995 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-freshwater-fresh-fish-basis-not-stated:b77bd623b8bb
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) Pb reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (canned) Pb reference · 1 sampling family. Fish, dry weight; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 12 | 12 | 12 |
| Alternative weighting | 12 | 12 | 12 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-canned-fish-dry-weight:6bebe814c0b1
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) Pb reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (canned) Pb reference · 1 sampling family. Fish, wet weight; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2 | ≤2 | ≤2 |
| Alternative weighting | ≤2 | ≤2 | ≤2 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-canned-fish-wet-weight:17677ac8a1c6
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) Pb reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (canned) Pb reference · 2 sampling families. Fish, basis not stated; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 16.1 |
| Alternative weighting | 10 | 10 | 16.1 |
8 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Dabeka et al. 1995 | 7 | 50% |
| European et al. 2004 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-canned-fish-basis-not-stated:b772f9a5d599
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (cooked) Pb reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (cooked) Pb reference · 2 sampling families. Fish, wet weight; Fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤3 | 3–4 (bounded) | 4–10 (bounded) |
| Alternative weighting | ≤3 | 3–4 (bounded) | 4–10 (bounded) |
36 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 34 | 50% |
| Baxter et al. 2015 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-cooked-fish-wet-weight:aff748759f9f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (cooked) Pb reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (cooked) Pb reference · 1 sampling family. Fish, basis not stated; Fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤10 | ≤10 |
| Alternative weighting | ≤10 | ≤10 | ≤10 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-cooked-fish-basis-not-stated:840a54b2024e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish oil) Pb reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish oil) Pb reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fish oil; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤25 | ≤84.6 | ≤100 |
| Alternative weighting | ≤25 | ≤84.6 | ≤100 |
6 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 6 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-fish-oil-fish-wet-weight:9878e8d8fc28
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) Pb reference · 3 sampling families
Reference and scope
HMI Fish, species not stated (fish product) Pb reference · 3 sampling families. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤4 | ≤4 | 5–10 (bounded) |
| Alternative weighting | ≤4 | ≤4 | 5–9 (bounded) |
37 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 34 | 33% |
| FDA TDS FY2018–FY2020 | 1 | 33% |
| Baxter et al. 2015 | 2 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-fish-product-fish-wet-weight:c43b6c91c0de
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish sauce) Pb reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish sauce) Pb reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fish sauce; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | 70–75 (bounded) | 140 |
| Alternative weighting | ≤10 | 70–75 (bounded) | 140 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-fish-sauce-fish-wet-weight:1322c26cab6f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish sauce) Pb reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish sauce) Pb reference · 1 sampling family. Fish, basis not stated; Fish, species not stated, fish sauce; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2580 | 3260 | 3940 |
| Alternative weighting | 2580 | 3260 | 3940 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Abdullah 2009 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-fish-sauce-fish-basis-not-stated:91fbfa1de70a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fresh or raw) Pb reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤6.67 | ≤10 | ≤16 |
| Alternative weighting | ≤6.67 | ≤10 | ≤16 |
50 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 50 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-fresh-fish-wet-weight:19eae0329e32
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) Pb reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fresh or raw) Pb reference · 1 sampling family. Fish, dry weight; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 80 | 80 | 80 |
| Alternative weighting | 80 | 80 | 80 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-fresh-fish-dry-weight:3f9312db8955
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) Pb reference · 3 sampling families
Reference and scope
HMI Fish, species not stated (fresh or raw) Pb reference · 3 sampling families. Fish, basis not stated; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2–6.8 (bounded) | 6.8–10 (bounded) | 140 |
| Alternative weighting | 2–6.8 (bounded) | 6.8–10 (bounded) | 140 |
7 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 5 | 33% |
| European et al. 2004 | 1 | 33% |
| Wang et al. 2019 | 1 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-fresh-fish-basis-not-stated:3e0728ac024c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (smoked, dried, salted or fermented) Pb reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (smoked, dried, salted or fermented) Pb reference · 1 sampling family. Fish, dry weight; Fish, species not stated, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 40 | 62.5 | 85 |
| Alternative weighting | 40 | 62.5 | 85 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-smoked-dried-salted-fermented-fish-dry-weight:b9cb59a3539a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (smoked, dried, salted or fermented) Pb reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (smoked, dried, salted or fermented) Pb reference · 1 sampling family. Fish, wet weight; Fish, species not stated, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 125 | 125 | 125 |
| Alternative weighting | 125 | 125 | 125 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-smoked-dried-salted-fermented-fish-wet-weight:6fe793144061
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (smoked, dried, salted or fermented) Pb reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (smoked, dried, salted or fermented) Pb reference · 1 sampling family. Fish, basis not stated; Fish, species not stated, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 970 | 1300 | 1400 |
| Alternative weighting | 970 | 1300 | 1400 |
5 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Bazie et al. 2022 | 5 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Pb-fish-unspecified-smoked-dried-salted-fermented-fish-basis-not-stated:13ed4ab8a73b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (canned) tAs reference · 3 sampling families
Reference and scope
HMI Tuna (canned) tAs reference · 3 sampling families. Fish, wet weight; Tuna, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 33 | 1200 | 1510 |
| Alternative weighting | 33 | 1200 | 1510 |
20 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 33% |
| De et al. 2021 | 16 | 33% |
| Olmedo et al. 2013 | 3 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-tuna-canned-fish-wet-weight:73f86230bc60
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (cooked) tAs reference · 1 sampling family
Reference and scope
HMI Tuna (cooked) tAs reference · 1 sampling family. Fish, wet weight; Tuna, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 658 | 920 | 1310 |
| Alternative weighting | 658 | 920 | 1310 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-tuna-cooked-fish-wet-weight:e32da0a07afb
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) tAs reference · 2 sampling families
Reference and scope
HMI Tuna (fresh or raw) tAs reference · 2 sampling families. Fish, wet weight; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 33 | 206 | 1000 |
| Alternative weighting | 33 | 206 | 1000 |
27 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 26 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-tuna-fresh-fish-wet-weight:22d1dd931098
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Tuna (fresh or raw) tAs reference · 1 sampling family. Fish, basis not stated; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 320 | 320 | 320 |
| Alternative weighting | 320 | 320 | 320 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-tuna-fresh-fish-basis-not-stated:7736f1d558cb
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Tuna (fresh or raw) tAs reference · 1 sampling family. Fish, dry weight; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2900 | 2900 | 2900 |
| Alternative weighting | 2900 | 2900 | 2900 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Brooke et al. 1981 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-tuna-fresh-fish-dry-weight:1a5f8a2d45cb
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Swordfish (fresh or raw) tAs reference · 2 sampling families
Reference and scope
HMI Swordfish (fresh or raw) tAs reference · 2 sampling families. Fish, wet weight; Swordfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 96 | 763 | 1430 |
| Alternative weighting | 96 | 763 | 1430 |
2 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-swordfish-fresh-fish-wet-weight:ce8d2705d5d7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shark (fresh or raw) tAs reference · 2 sampling families
Reference and scope
HMI Shark (fresh or raw) tAs reference · 2 sampling families. Fish, wet weight; Shark, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 242 | 822 | 7000 |
| Alternative weighting | 242 | 822 | 7000 |
27 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Sang et al. 2019 | 25 | 50% |
| Olmedo et al. 2013 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-shark-fresh-fish-wet-weight:f50c6580285e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (canned) tAs reference · 1 sampling family
Reference and scope
HMI Mackerel (canned) tAs reference · 1 sampling family. Fish, wet weight; Mackerel, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 52 | 52 | 52 |
| Alternative weighting | 52 | 52 | 52 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-mackerel-canned-fish-wet-weight:1c791c3831c8
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) tAs reference · 2 sampling families
Reference and scope
HMI Mackerel (fresh or raw) tAs reference · 2 sampling families. Fish, wet weight; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 190 | 190 | 1500 |
| Alternative weighting | 190 | 190 | 1500 |
31 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 30 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-mackerel-fresh-fish-wet-weight:a29ab3beada8
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Mackerel (fresh or raw) tAs reference · 1 sampling family. Fish, basis not stated; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 790 | 790 | 790 |
| Alternative weighting | 790 | 790 | 790 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| European et al. 2004 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-mackerel-fresh-fish-basis-not-stated:23c4ea756a8e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Horse mackerel, jacks and trevally (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Horse mackerel, jacks and trevally (fresh or raw) tAs reference · 1 sampling family. Fish, basis not stated; Horse mackerel, jacks and trevally, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1360 | 1360 | 1360 |
| Alternative weighting | 1360 | 1360 | 1360 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-horse-mackerel-jack-fresh-fish-basis-not-stated:d5e08109428d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Horse mackerel, jacks and trevally (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Horse mackerel, jacks and trevally (fresh or raw) tAs reference · 1 sampling family. Fish, wet weight; Horse mackerel, jacks and trevally, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 243 | 243 | 243 |
| Alternative weighting | 243 | 243 | 243 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-horse-mackerel-jack-fresh-fish-wet-weight:ea64fa3864c0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Herring (fresh or raw) tAs reference · 1 sampling family. Fish, wet weight; Herring, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1130 | 1510 | 1790 |
| Alternative weighting | 1130 | 1510 | 1790 |
36 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 36 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-herring-fresh-fish-wet-weight:5849932a3cf7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Herring (fresh or raw) tAs reference · 1 sampling family. Fish, basis not stated; Herring, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1100 | 1100 | 1100 |
| Alternative weighting | 1100 | 1100 | 1100 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Brooke et al. 1981 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-herring-fresh-fish-basis-not-stated:df6118eb9843
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (canned) tAs reference · 2 sampling families
Reference and scope
HMI Sardine and pilchard (canned) tAs reference · 2 sampling families. Fish, wet weight; Sardine and pilchard, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 103 | 1290 | 3170 |
| Alternative weighting | 103 | 1290 | 3170 |
12 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| De et al. 2021 | 10 | 50% |
| Olmedo et al. 2013 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-sardine-pilchard-canned-fish-wet-weight:a1ce61f7993f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) tAs reference · 2 sampling families
Reference and scope
HMI Sardine and pilchard (fresh or raw) tAs reference · 2 sampling families. Fish, wet weight; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 561 | 561 | 2240 |
| Alternative weighting | 561 | 561 | 2240 |
24 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 23 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-sardine-pilchard-fresh-fish-wet-weight:7b996b91ed9d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (fresh or raw) tAs reference · 1 sampling family. Fish, basis not stated; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 4510 | 4510 | 4510 |
| Alternative weighting | 4510 | 4510 | 4510 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-sardine-pilchard-fresh-fish-basis-not-stated:261ecbdd1110
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (fresh or raw) tAs reference · 1 sampling family. Fish, dry weight; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 16700 | 16700 | 16700 |
| Alternative weighting | 16700 | 16700 | 16700 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Munoz et al. 1999 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-sardine-pilchard-fresh-fish-dry-weight:ba01f74e2372
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (canned) tAs reference · 1 sampling family
Reference and scope
HMI Anchovy (canned) tAs reference · 1 sampling family. Fish, wet weight; Anchovy, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 159 | 159 | 159 |
| Alternative weighting | 159 | 159 | 159 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-anchovy-canned-fish-wet-weight:5c89b544ae85
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Anchovy (fresh or raw) tAs reference · 1 sampling family. Fish, wet weight; Anchovy, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 188 | 188 | 188 |
| Alternative weighting | 188 | 188 | 188 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-anchovy-fresh-fish-wet-weight:4a8c16088cb9
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Anchovy (fresh or raw) tAs reference · 1 sampling family. Fish, basis not stated; Anchovy, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2330 | 2330 | 2330 |
| Alternative weighting | 2330 | 2330 | 2330 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-anchovy-fresh-fish-basis-not-stated:ebe5e58671b1
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Anchovy (fresh or raw) tAs reference · 1 sampling family. Fish, dry weight; Anchovy, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 18800 | 18800 | 18800 |
| Alternative weighting | 18800 | 18800 | 18800 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Munoz et al. 1999 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-anchovy-fresh-fish-dry-weight:666b6f41df1f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shad, hilsa and other herrings (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Shad, hilsa and other herrings (fresh or raw) tAs reference · 1 sampling family. Fish, basis not stated; Shad, hilsa and other herrings, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1300 | 1300 | 1300 |
| Alternative weighting | 1300 | 1300 | 1300 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-shad-other-clupeid-fresh-fish-basis-not-stated:d488b0752467
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (canned) tAs reference · 1 sampling family
Reference and scope
HMI Salmon (canned) tAs reference · 1 sampling family. Fish, wet weight; Salmon, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 237 | 237 | 237 |
| Alternative weighting | 237 | 237 | 237 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-salmon-canned-fish-wet-weight:fc28e4934a0b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (cooked) tAs reference · 2 sampling families
Reference and scope
HMI Salmon (cooked) tAs reference · 2 sampling families. Fish, wet weight; Salmon, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 240 | 733 | 1280 |
| Alternative weighting | 240 | 733 | 1280 |
4 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 50% |
| FDA TDS FY2018–FY2020 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-salmon-cooked-fish-wet-weight:89aeecfb684c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (fresh or raw) tAs reference · 2 sampling families
Reference and scope
HMI Salmon (fresh or raw) tAs reference · 2 sampling families. Fish, wet weight; Salmon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 47 | 47 | 148 |
| Alternative weighting | 47 | 47 | 148 |
9 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 8 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-salmon-fresh-fish-wet-weight:2a043a40f03d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) tAs reference · 2 sampling families
Reference and scope
HMI Trout and char (fresh or raw) tAs reference · 2 sampling families. Fish, wet weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 373 | 2000 | 2000 |
| Alternative weighting | 373 | 2000 | 2000 |
37 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 36 | 50% |
| Groleau et al. 2025 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-trout-fresh-fish-wet-weight:2c9cc8d6d63a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) tAs reference · 1 sampling family. Fish, dry weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 4520 | 4670 | 4820 |
| Alternative weighting | 4520 | 4670 | 4820 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Total Arsenic and… 2019 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-trout-fresh-fish-dry-weight:720b5e49b0d1
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (cooked) tAs reference · 1 sampling family
Reference and scope
HMI Cod (cooked) tAs reference · 1 sampling family. Fish, wet weight; Cod, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 4500 | 4500 | 4500 |
| Alternative weighting | 4500 | 4500 | 4500 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-cod-cooked-fish-wet-weight:0abc1833418b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fish oil) tAs reference · 1 sampling family
Reference and scope
HMI Cod (fish oil) tAs reference · 1 sampling family. Fish, wet weight; Cod, fish oil; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤75 | ≤75 | ≤75 |
| Alternative weighting | ≤75 | ≤75 | ≤75 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-cod-fish-oil-fish-wet-weight:d880f3c734cc
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fresh or raw) tAs reference · 2 sampling families
Reference and scope
HMI Cod (fresh or raw) tAs reference · 2 sampling families. Fish, wet weight; Cod, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 36 | 208 | 3070 |
| Alternative weighting | 36 | 208 | 3070 |
32 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 31 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-cod-fresh-fish-wet-weight:48b3331ec11d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Haddock (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Haddock (fresh or raw) tAs reference · 1 sampling family. Fish, basis not stated; Haddock, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2600 | 2600 | 2600 |
| Alternative weighting | 2600 | 2600 | 2600 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Brooke et al. 1981 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-haddock-fresh-fish-basis-not-stated:4036aed06995
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Pollock and saithe (fish product) tAs reference · 1 sampling family
Reference and scope
HMI Pollock and saithe (fish product) tAs reference · 1 sampling family. Fish, wet weight; Pollock and saithe, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1900 | 3050 | 4200 |
| Alternative weighting | 1900 | 3050 | 4200 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Naess et al. 2020 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-pollock-saithe-fish-product-fish-wet-weight:526f13421700
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Whiting and blue whiting (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Whiting and blue whiting (fresh or raw) tAs reference · 1 sampling family. Fish, wet weight; Whiting and blue whiting, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 134 | 134 | 134 |
| Alternative weighting | 134 | 134 | 134 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-whiting-blue-whiting-fresh-fish-wet-weight:5b06abb37d6a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hake (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Hake (fresh or raw) tAs reference · 1 sampling family. Fish, wet weight; Hake, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 28 | 48 | 165 |
| Alternative weighting | 28 | 48 | 165 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-hake-fresh-fish-wet-weight:ec4366ce3959
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (fresh or raw) tAs reference · 2 sampling families
Reference and scope
HMI Plaice, flounder, sole and turbot (fresh or raw) tAs reference · 2 sampling families. Fish, basis not stated; Plaice, flounder, sole and turbot, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2300 | 13200 | 24000 |
| Alternative weighting | 2300 | 13200 | 24000 |
2 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Brooke et al. 1981 | 1 | 50% |
| Kaise et al. 1988 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-plaice-flounder-sole-fresh-fish-basis-not-stated:5d69e39aea51
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Plaice, flounder, sole and turbot (fresh or raw) tAs reference · 1 sampling family. Fish, wet weight; Plaice, flounder, sole and turbot, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 59 | 66 | 233 |
| Alternative weighting | 59 | 66 | 233 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-plaice-flounder-sole-fresh-fish-wet-weight:f1eb62a4bc4a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Halibut (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Halibut (fresh or raw) tAs reference · 1 sampling family. Fish, basis not stated; Halibut, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1910 | 1910 | 1910 |
| Alternative weighting | 1910 | 1910 | 1910 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-halibut-fresh-fish-basis-not-stated:e0a204e08252
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bass and barramundi (fresh or raw) tAs reference · 2 sampling families
Reference and scope
HMI Sea bass and barramundi (fresh or raw) tAs reference · 2 sampling families. Fish, wet weight; Sea bass and barramundi, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 25 | 65 | 105 |
| Alternative weighting | 25 | 65 | 105 |
2 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Cirillo et al. 2010 | 1 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-sea-bass-fresh-fish-wet-weight:5a33bfcfa5ab
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bream and porgies (fresh or raw) tAs reference · 2 sampling families
Reference and scope
HMI Sea bream and porgies (fresh or raw) tAs reference · 2 sampling families. Fish, wet weight; Sea bream and porgies, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 103 | 1290 | 4520 |
| Alternative weighting | 103 | 1290 | 4520 |
4 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 3 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-sea-bream-porgy-fresh-fish-wet-weight:30aaca28f97f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bream and porgies (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Sea bream and porgies (fresh or raw) tAs reference · 1 sampling family. Fish, basis not stated; Sea bream and porgies, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1210 | 1210 | 1210 |
| Alternative weighting | 1210 | 1210 | 1210 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-sea-bream-porgy-fresh-fish-basis-not-stated:67441da5120a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Red mullet and goatfish (fresh or raw) tAs reference · 2 sampling families
Reference and scope
HMI Red mullet and goatfish (fresh or raw) tAs reference · 2 sampling families. Fish, wet weight; Red mullet and goatfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 127 | 277 | 427 |
| Alternative weighting | 127 | 277 | 427 |
2 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Cirillo et al. 2010 | 1 | 50% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-red-mullet-goatfish-fresh-fish-wet-weight:6032fa3d7b6b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Grey mullet (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Grey mullet (fresh or raw) tAs reference · 1 sampling family. Fish, basis not stated; Grey mullet, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 497 | 497 | 497 |
| Alternative weighting | 497 | 497 | 497 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Bakhshalizadeh et al. 2023 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-grey-mullet-fresh-fish-basis-not-stated:1e3c7e1b8fec
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Emperors and grunts (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Emperors and grunts (fresh or raw) tAs reference · 1 sampling family. Fish, basis not stated; Emperors and grunts, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 620 | 620 | 620 |
| Alternative weighting | 620 | 620 | 620 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-emperor-grunt-fresh-fish-basis-not-stated:d128fd74257d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Barracuda (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Barracuda (fresh or raw) tAs reference · 1 sampling family. Fish, wet weight; Barracuda, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1370 | 1370 | 1370 |
| Alternative weighting | 1370 | 1370 | 1370 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-barracuda-fresh-fish-wet-weight:6a34663912ea
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Barracuda (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Barracuda (fresh or raw) tAs reference · 1 sampling family. Fish, basis not stated; Barracuda, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 880 | 880 | 880 |
| Alternative weighting | 880 | 880 | 880 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-barracuda-fresh-fish-basis-not-stated:2ff2a1f07c77
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anglerfish and monkfish (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Anglerfish and monkfish (fresh or raw) tAs reference · 1 sampling family. Fish, wet weight; Anglerfish and monkfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 43 | 43 | 43 |
| Alternative weighting | 43 | 43 | 43 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-anglerfish-monkfish-fresh-fish-wet-weight:392a3eeb3e72
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Gurnard (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Gurnard (fresh or raw) tAs reference · 1 sampling family. Fish, wet weight; Gurnard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 4410 | 4410 | 4410 |
| Alternative weighting | 4410 | 4410 | 4410 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-gurnard-fresh-fish-wet-weight:508ebbfb0cb4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sturgeon (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Sturgeon (fresh or raw) tAs reference · 1 sampling family. Fish, dry weight; Sturgeon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5930 | 5930 | 5930 |
| Alternative weighting | 5930 | 5930 | 5930 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Total Arsenic and… 2019 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-sturgeon-fresh-fish-dry-weight:e07bbb12581e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other marine fish (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Other marine fish (fresh or raw) tAs reference · 1 sampling family. Fish, basis not stated; Other marine fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 470 | 730 | 4350 |
| Alternative weighting | 470 | 730 | 4350 |
6 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 6 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-other-marine-finfish-fresh-fish-basis-not-stated:cba0b63017cd
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tilapia (cooked) tAs reference · 1 sampling family
Reference and scope
HMI Tilapia (cooked) tAs reference · 1 sampling family. Fish, wet weight; Tilapia, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 100 | 100 | 100 |
| Alternative weighting | 100 | 100 | 100 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-tilapia-cooked-fish-wet-weight:08e2dbab3367
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (fresh or raw) tAs reference · 1 sampling family. Fish, wet weight; Carp and other cyprinids, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 34.5 | 41.5 |
| Alternative weighting | 30 | 34.5 | 41.5 |
5 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 5 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-carp-cyprinid-fresh-fish-wet-weight:56282fd8028c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (fresh or raw) tAs reference · 1 sampling family. Fish, basis not stated; Carp and other cyprinids, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 120 | 120 | 120 |
| Alternative weighting | 120 | 120 | 120 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Subhanullah et al. 2024 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-carp-cyprinid-fresh-fish-basis-not-stated:ae380ba40b18
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (fresh or raw) tAs reference · 1 sampling family. Fish, dry weight; Carp and other cyprinids, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 90 | 116 | 379 |
| Alternative weighting | 90 | 116 | 379 |
5 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Total Arsenic and… 2019 | 5 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-carp-cyprinid-fresh-fish-dry-weight:748c89e41c87
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Catfish (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Catfish (fresh or raw) tAs reference · 1 sampling family. Fish, wet weight; Catfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 21 | 21 | 21 |
| Alternative weighting | 21 | 21 | 21 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-catfish-fresh-fish-wet-weight:456385c017e9
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other freshwater fish (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Other freshwater fish (fresh or raw) tAs reference · 1 sampling family. Fish, wet weight; Other freshwater fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2 | 2 | 2 |
| Alternative weighting | 2 | 2 | 2 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-other-freshwater-finfish-fresh-fish-wet-weight:4fcb4e5932dd
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (cooked) tAs reference · 2 sampling families
Reference and scope
HMI Marine fish, species not stated (cooked) tAs reference · 2 sampling families. Fish, wet weight; Marine fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2370 | 8830 | 14000 |
| Alternative weighting | 2370 | 8830 | 14000 |
3 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 50% |
| Ventura et al. 2025 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-fish-unspecified-marine-cooked-fish-wet-weight:af97b4876460
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) tAs reference · 2 sampling families
Reference and scope
HMI Marine fish, species not stated (fresh or raw) tAs reference · 2 sampling families. Fish, wet weight; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 81 | 82–91 (bounded) | 1710 |
| Alternative weighting | 81 | 82–91 (bounded) | 1710 |
15 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 12 | 50% |
| Cirillo et al. 2010 | 3 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-fish-unspecified-marine-fresh-fish-wet-weight:2ba9658aa0bd
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (cooked) tAs reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (cooked) tAs reference · 1 sampling family. Fish, wet weight; Freshwater fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 16 | 16 | 16 |
| Alternative weighting | 16 | 16 | 16 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-fish-unspecified-freshwater-cooked-fish-wet-weight:2bb48a2f644d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (fresh or raw) tAs reference · 1 sampling family. Fish, wet weight; Freshwater fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤49.5 | 30–100 (bounded) | 74–100 (bounded) |
| Alternative weighting | ≤49.5 | 30–100 (bounded) | 74–100 (bounded) |
15 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 15 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-fish-unspecified-freshwater-fresh-fish-wet-weight:c62a4449ef98
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) tAs reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (canned) tAs reference · 2 sampling families. Fish, wet weight; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 831 | 831 | 1120 |
| Alternative weighting | 831 | 831 | 1120 |
11 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 10 | 50% |
| Baxter et al. 2015 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-fish-unspecified-canned-fish-wet-weight:bb12e0ab1642
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (cooked) tAs reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (cooked) tAs reference · 2 sampling families. Fish, wet weight; Fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 957 | 1080 | 3220 |
| Alternative weighting | 957 | 1080 | 3220 |
20 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 18 | 50% |
| Baxter et al. 2015 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-fish-unspecified-cooked-fish-wet-weight:9787dd46b046
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) tAs reference · 3 sampling families
Reference and scope
HMI Fish, species not stated (fish product) tAs reference · 3 sampling families. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 810 | 1130 | 1400 |
| Alternative weighting | 810 | 1140 | 1400 |
17 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 14 | 33% |
| FDA TDS FY2018–FY2020 | 1 | 33% |
| Baxter et al. 2015 | 2 | 33% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-fish-unspecified-fish-product-fish-wet-weight:d89a55870bb3
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish sauce) tAs reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish sauce) tAs reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fish sauce; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 940 | 940 | 940 |
| Alternative weighting | 940 | 940 | 940 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-fish-unspecified-fish-sauce-fish-wet-weight:b8ad2f84e2b8
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) tAs reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fresh or raw) tAs reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 96–100 (bounded) | 422 | 728 |
| Alternative weighting | 76–83.3 (bounded) | 294 | 728 |
58 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 58 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-fish-unspecified-fresh-fish-wet-weight:75af1b4db8c3
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (smoked, dried, salted or fermented) tAs reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (smoked, dried, salted or fermented) tAs reference · 1 sampling family. Fish, wet weight; Fish, species not stated, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1040 | 1680 | 1900 |
| Alternative weighting | 1040 | 1620 | 1870 |
11 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 11 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-tAs-fish-unspecified-smoked-dried-salted-fermented-fish-wet-weight:daf1874a4f23
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (cooked) iAs reference · 1 sampling family
Reference and scope
HMI Tuna (cooked) iAs reference · 1 sampling family. Fish, wet weight; Tuna, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤4.5 | 2–7.5 (bounded) | 4.5–15 (bounded) |
| Alternative weighting | ≤4.5 | 2–7.5 (bounded) | 4.5–15 (bounded) |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-tuna-cooked-fish-wet-weight:854e50b4e4cd
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Tuna (fresh or raw) iAs reference · 1 sampling family. Fish, wet weight; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤8.4 | ≤20 | ≤20 |
| Alternative weighting | ≤8.4 | ≤20 | ≤20 |
10 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 10 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-tuna-fresh-fish-wet-weight:5aaa92c3951b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) iAs reference · 2 sampling families
Reference and scope
HMI Tuna (fresh or raw) iAs reference · 2 sampling families. Fish, dry weight; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 0.17–0.53 (bounded) | 60.2–60.3 (bounded) | 140 |
| Alternative weighting | 0.17–0.53 (bounded) | 60.2–60.3 (bounded) | 140 |
6 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 50% |
| Brooke et al. 1981 | 4 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-tuna-fresh-fish-dry-weight:e95c9c613251
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (cooked) iAs reference · 1 sampling family
Reference and scope
HMI Mackerel (cooked) iAs reference · 1 sampling family. Fish, wet weight; Mackerel, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤20 | ≤20 |
| Alternative weighting | ≤20 | ≤20 | ≤20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-mackerel-cooked-fish-wet-weight:e61e1e3270d9
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Mackerel (fresh or raw) iAs reference · 1 sampling family. Fish, wet weight; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤30 | 15.5–39.1 (bounded) |
| Alternative weighting | ≤20 | ≤30 | 15.5–39.1 (bounded) |
12 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 12 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-mackerel-fresh-fish-wet-weight:fa0b24fd4505
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Mackerel (fresh or raw) iAs reference · 1 sampling family. Fish, dry weight; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤0.078 | ≤0.379 | ≤0.68 |
| Alternative weighting | ≤0.078 | ≤0.379 | ≤0.68 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-mackerel-fresh-fish-dry-weight:6184d113df98
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Mackerel (fresh or raw) iAs reference · 1 sampling family. Fish, basis not stated; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 26.5 | 68 | 100 |
| Alternative weighting | 26.5 | 68 | 100 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-mackerel-fresh-fish-basis-not-stated:b66e9ff83791
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (fresh or raw) iAs reference · 2 sampling families
Reference and scope
HMI Herring (fresh or raw) iAs reference · 2 sampling families. Fish, wet weight; Herring, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤30 | 30–70 (bounded) | 90 |
| Alternative weighting | ≤30 | 30–70 (bounded) | 90 |
13 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 9 | 50% |
| Norin et al. 1985 | 4 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-herring-fresh-fish-wet-weight:72400defb974
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Herring (fresh or raw) iAs reference · 1 sampling family. Fish, dry weight; Herring, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤0.078 | 0.268–0.476 (bounded) | 0.535–0.875 (bounded) |
| Alternative weighting | ≤0.078 | 0.268–0.476 (bounded) | 0.535–0.875 (bounded) |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-herring-fresh-fish-dry-weight:1fb1088c75db
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Herring (fresh or raw) iAs reference · 1 sampling family. Fish, basis not stated; Herring, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 40 | 40 |
| Alternative weighting | 30 | 40 | 40 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Brooke et al. 1981 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-herring-fresh-fish-basis-not-stated:941602664d39
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (cooked) iAs reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (cooked) iAs reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 28 | 28 | 28 |
| Alternative weighting | 28 | 28 | 28 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-sardine-pilchard-cooked-fish-wet-weight:23a079a86943
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (fresh or raw) iAs reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤13.1 | 8.8–36 (bounded) | 56 |
| Alternative weighting | ≤13.1 | 8.8–36 (bounded) | 56 |
11 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 11 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-sardine-pilchard-fresh-fish-wet-weight:3d99488e121b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (fresh or raw) iAs reference · 1 sampling family. Fish, dry weight; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 99 | 118 | 137 |
| Alternative weighting | 99 | 118 | 137 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Munoz et al. 1999 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-sardine-pilchard-fresh-fish-dry-weight:5080f0264c7f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Anchovy (fresh or raw) iAs reference · 1 sampling family. Fish, dry weight; Anchovy, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 123 | 150 | 176 |
| Alternative weighting | 123 | 150 | 176 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Munoz et al. 1999 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-anchovy-fresh-fish-dry-weight:4cc715dcbc55
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (canned) iAs reference · 1 sampling family
Reference and scope
HMI Salmon (canned) iAs reference · 1 sampling family. Fish, wet weight; Salmon, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤12 | ≤12 | ≤12 |
| Alternative weighting | ≤12 | ≤12 | ≤12 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-salmon-canned-fish-wet-weight:d84169ffe5c0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (cooked) iAs reference · 1 sampling family
Reference and scope
HMI Salmon (cooked) iAs reference · 1 sampling family. Fish, wet weight; Salmon, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤20 | ≤20 |
| Alternative weighting | ≤20 | ≤20 | ≤20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-salmon-cooked-fish-wet-weight:22facddbb6d0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Salmon (fresh or raw) iAs reference · 1 sampling family. Fish, dry weight; Salmon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1.25 | 1.29 | 1.33 |
| Alternative weighting | 1.25 | 1.29 | 1.33 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-salmon-fresh-fish-dry-weight:2adc0c30e85a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Salmon (fresh or raw) iAs reference · 1 sampling family. Fish, wet weight; Salmon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤20 | ≤20 |
| Alternative weighting | ≤20 | ≤20 | ≤20 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-salmon-fresh-fish-wet-weight:4b13e68d822e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) iAs reference · 1 sampling family. Fish, wet weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤3.91 | ≤4.95 | ≤7.52 |
| Alternative weighting | ≤3.91 | ≤4.95 | ≤7.52 |
8 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 8 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-trout-fresh-fish-wet-weight:d5be445b6f29
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) iAs reference · 1 sampling family. Fish, dry weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 0.87 | 0.87 | 0.87 |
| Alternative weighting | 0.87 | 0.87 | 0.87 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-trout-fresh-fish-dry-weight:9490ec477fc0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Cod (fresh or raw) iAs reference · 1 sampling family. Fish, wet weight; Cod, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤6.7 | ≤20 | ≤36 |
| Alternative weighting | ≤6.7 | ≤20 | ≤36 |
14 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 14 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-cod-fresh-fish-wet-weight:efcafe49c4d8
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Cod (fresh or raw) iAs reference · 1 sampling family. Fish, dry weight; Cod, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤0.68 | ≤0.68 | ≤0.68 |
| Alternative weighting | ≤0.68 | ≤0.68 | ≤0.68 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-cod-fresh-fish-dry-weight:b7340aa490ae
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Haddock (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Haddock (fresh or raw) iAs reference · 1 sampling family. Fish, basis not stated; Haddock, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 20 | 30 |
| Alternative weighting | 20 | 20 | 30 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Brooke et al. 1981 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-haddock-fresh-fish-basis-not-stated:4af4267eff63
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (cooked) iAs reference · 1 sampling family
Reference and scope
HMI Plaice, flounder, sole and turbot (cooked) iAs reference · 1 sampling family. Fish, wet weight; Plaice, flounder, sole and turbot, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤3 | 2.5–4 (bounded) | 5 |
| Alternative weighting | ≤3 | 2.5–4 (bounded) | 5 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-plaice-flounder-sole-cooked-fish-wet-weight:321620729077
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Plaice, flounder, sole and turbot (fresh or raw) iAs reference · 1 sampling family. Fish, basis not stated; Plaice, flounder, sole and turbot, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10–20 (bounded) | 20 | 30 |
| Alternative weighting | 10–20 (bounded) | 20 | 30 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Brooke et al. 1981 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-plaice-flounder-sole-fresh-fish-basis-not-stated:681595c8b182
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Croaker and drum (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Croaker and drum (fresh or raw) iAs reference · 1 sampling family. Fish, basis not stated; Croaker and drum, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 33 | 36.5 | 40 |
| Alternative weighting | 33 | 36.5 | 40 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-croaker-drum-fresh-fish-basis-not-stated:5da9d9e3b162
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Croaker and drum (smoked, dried, salted or fermented) iAs reference · 1 sampling family
Reference and scope
HMI Croaker and drum (smoked, dried, salted or fermented) iAs reference · 1 sampling family. Fish, basis not stated; Croaker and drum, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2.5 | 10.5–11.8 (bounded) | 21 |
| Alternative weighting | ≤2.5 | 10.5–11.8 (bounded) | 21 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-croaker-drum-smoked-dried-salted-fermented-fish-basis-not-stated:fcd30455d3ca
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hairtail and cutlassfish (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Hairtail and cutlassfish (fresh or raw) iAs reference · 1 sampling family. Fish, basis not stated; Hairtail and cutlassfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 4.3–5.55 (bounded) | 16.8 | 37.5 |
| Alternative weighting | 4.3–5.55 (bounded) | 16.8 | 37.5 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-hairtail-cutlassfish-fresh-fish-basis-not-stated:75b395d9d89b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hairtail and cutlassfish (smoked, dried, salted or fermented) iAs reference · 1 sampling family
Reference and scope
HMI Hairtail and cutlassfish (smoked, dried, salted or fermented) iAs reference · 1 sampling family. Fish, basis not stated; Hairtail and cutlassfish, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2.5 | 3.55–4.8 (bounded) | 7.1 |
| Alternative weighting | ≤2.5 | 3.55–4.8 (bounded) | 7.1 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-hairtail-cutlassfish-smoked-dried-salted-fermented-fish-basis-not-stated:3cc8b84c6675
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other marine fish (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Other marine fish (fresh or raw) iAs reference · 1 sampling family. Fish, wet weight; Other marine fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 50 | 75 | 115 |
| Alternative weighting | 50 | 75 | 115 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Norin et al. 1985 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-other-marine-finfish-fresh-fish-wet-weight:bfe6911e8160
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (cooked) iAs reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (cooked) iAs reference · 1 sampling family. Fish, wet weight; Carp and other cyprinids, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤3 | ≤3 | ≤3 |
| Alternative weighting | ≤3 | ≤3 | ≤3 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-carp-cyprinid-cooked-fish-wet-weight:2417a7c5d6a6
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (fresh or raw) iAs reference · 1 sampling family. Fish, wet weight; Carp and other cyprinids, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 20 |
| Alternative weighting | 10 | 10 | 20 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Norin et al. 1985 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-carp-cyprinid-fresh-fish-wet-weight:0ff80b9e342e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Pike (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Pike (fresh or raw) iAs reference · 1 sampling family. Fish, wet weight; Pike, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 20 | 25 |
| Alternative weighting | 10 | 20 | 25 |
8 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Norin et al. 1985 | 8 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-pike-fresh-fish-wet-weight:c600da993a95
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Perch, walleye and zander (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Perch, walleye and zander (fresh or raw) iAs reference · 1 sampling family. Fish, wet weight; Perch, walleye and zander, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 15 | 20 |
| Alternative weighting | 10 | 15 | 20 |
8 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Norin et al. 1985 | 8 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-perch-walleye-fresh-fish-wet-weight:14001db9b87a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other freshwater fish (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Other freshwater fish (fresh or raw) iAs reference · 1 sampling family. Fish, wet weight; Other freshwater fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 40 | 50 |
| Alternative weighting | 30 | 40 | 50 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Norin et al. 1985 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-other-freshwater-finfish-fresh-fish-wet-weight:815e57b90dfd
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Bream (species group not stated) (cooked) iAs reference · 1 sampling family
Reference and scope
HMI Bream (species group not stated) (cooked) iAs reference · 1 sampling family. Fish, wet weight; Bream (species group not stated), cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 21.5 | 21.5 | 21.5 |
| Alternative weighting | 21.5 | 21.5 | 21.5 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-bream-unspecified-cooked-fish-wet-weight:e3c5f1be1539
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (cooked) iAs reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (cooked) iAs reference · 1 sampling family. Fish, wet weight; Marine fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | 22–32 (bounded) | 44 |
| Alternative weighting | ≤20 | 22–32 (bounded) | 44 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-fish-unspecified-marine-cooked-fish-wet-weight:630cda9b6db6
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (fresh or raw) iAs reference · 1 sampling family. Fish, wet weight; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤16 | ≤20 |
| Alternative weighting | ≤10 | ≤16 | ≤20 |
14 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 14 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-fish-unspecified-marine-fresh-fish-wet-weight:9c778b4bd0a9
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (fresh or raw) iAs reference · 1 sampling family. Fish, dry weight; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤0.078 | 0.962–1 (bounded) | 1.92 |
| Alternative weighting | ≤0.078 | 0.962–1 (bounded) | 1.92 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-fish-unspecified-marine-fresh-fish-dry-weight:08a163f0fd35
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (cooked) iAs reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (cooked) iAs reference · 1 sampling family. Fish, wet weight; Freshwater fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤20 | ≤20 |
| Alternative weighting | ≤20 | ≤20 | ≤20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-fish-unspecified-freshwater-cooked-fish-wet-weight:c34fd8f0f89f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (fresh or raw) iAs reference · 1 sampling family. Fish, wet weight; Freshwater fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤20 | ≤20 |
| Alternative weighting | ≤10 | ≤20 | ≤20 |
10 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 10 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-fish-unspecified-freshwater-fresh-fish-wet-weight:176cc409ec38
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (fresh or raw) iAs reference · 1 sampling family. Fish, dry weight; Freshwater fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 0.51–0.85 (bounded) | 0.51–0.85 (bounded) | 0.51–0.85 (bounded) |
| Alternative weighting | 0.51–0.85 (bounded) | 0.51–0.85 (bounded) | 0.51–0.85 (bounded) |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-fish-unspecified-freshwater-fresh-fish-dry-weight:ab53ea75ad2a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) iAs reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (canned) iAs reference · 2 sampling families. Fish, wet weight; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤12 | ≤12 | ≤18.5 |
| Alternative weighting | ≤12 | ≤12 | ≤18.5 |
10 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 9 | 50% |
| Baxter et al. 2015 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-fish-unspecified-canned-fish-wet-weight:72ee5f0da699
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (cooked) iAs reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (cooked) iAs reference · 2 sampling families. Fish, wet weight; Fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 6.5–10 (bounded) | 14 | 15 |
| Alternative weighting | 6.5–10 (bounded) | 14 | 15 |
5 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 50% |
| Baxter et al. 2015 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-fish-unspecified-cooked-fish-wet-weight:98e782654345
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) iAs reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (fish product) iAs reference · 2 sampling families. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤12 | ≤16 | ≤20 |
| Alternative weighting | ≤12 | ≤16 | ≤20 |
6 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 4 | 50% |
| Baxter et al. 2015 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-fish-unspecified-fish-product-fish-wet-weight:82fd742f3762
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) iAs reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fresh or raw) iAs reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤5 | ≤10.1 | ≤30 |
| Alternative weighting | ≤5.39 | ≤10.3 | ≤33 |
20 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 20 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-fish-unspecified-fresh-fish-wet-weight:0792ab98db20
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (smoked, dried, salted or fermented) iAs reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (smoked, dried, salted or fermented) iAs reference · 1 sampling family. Fish, wet weight; Fish, species not stated, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤8 | ≤20 | 80 |
| Alternative weighting | ≤10.3 | ≤20.5 | 80 |
11 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 11 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-iAs-fish-unspecified-smoked-dried-salted-fermented-fish-wet-weight:853509a6903d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Tuna (fresh or raw) DMA reference · 1 sampling family. Fish, basis not stated; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 10 |
| Alternative weighting | 10 | 10 | 10 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-tuna-fresh-fish-basis-not-stated:b896b4585554
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Mackerel (fresh or raw) DMA reference · 1 sampling family. Fish, basis not stated; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 32 | 38 | 44 |
| Alternative weighting | 32 | 38 | 44 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-mackerel-fresh-fish-basis-not-stated:0e31252b2c63
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Horse mackerel, jacks and trevally (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Horse mackerel, jacks and trevally (fresh or raw) DMA reference · 1 sampling family. Fish, basis not stated; Horse mackerel, jacks and trevally, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 10 |
| Alternative weighting | 10 | 10 | 10 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-horse-mackerel-jack-fresh-fish-basis-not-stated:d75d54d2e53c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (fresh or raw) DMA reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | 11–21 (bounded) | 22 |
| Alternative weighting | ≤20 | 11–21 (bounded) | 22 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-sardine-pilchard-fresh-fish-wet-weight:912c3e99ef62
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (fresh or raw) DMA reference · 1 sampling family. Fish, basis not stated; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 10 |
| Alternative weighting | 10 | 10 | 10 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-sardine-pilchard-fresh-fish-basis-not-stated:05d985892a72
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Anchovy (fresh or raw) DMA reference · 1 sampling family. Fish, basis not stated; Anchovy, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 10 |
| Alternative weighting | 10 | 10 | 10 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-anchovy-fresh-fish-basis-not-stated:64e47bcbf3e3
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shad, hilsa and other herrings (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Shad, hilsa and other herrings (fresh or raw) DMA reference · 1 sampling family. Fish, basis not stated; Shad, hilsa and other herrings, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 20 | 20 |
| Alternative weighting | 20 | 20 | 20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-shad-other-clupeid-fresh-fish-basis-not-stated:a1cc6d4a34e5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) DMA reference · 1 sampling family. Fish, wet weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤2.48 | ≤6.24 | ≤10 |
| Alternative weighting | ≤2.48 | ≤6.24 | ≤10 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-trout-fresh-fish-wet-weight:a797b72bccb7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Cod (fresh or raw) DMA reference · 1 sampling family. Fish, wet weight; Cod, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤11.4 | ≤12.8 |
| Alternative weighting | ≤10 | ≤11.4 | ≤12.8 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-cod-fresh-fish-wet-weight:746dd2975724
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Plaice, flounder, sole and turbot (fresh or raw) DMA reference · 1 sampling family. Fish, basis not stated; Plaice, flounder, sole and turbot, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 30 | 30 | 30 |
| Alternative weighting | 30 | 30 | 30 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-plaice-flounder-sole-fresh-fish-basis-not-stated:a0bbcae45a14
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Halibut (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Halibut (fresh or raw) DMA reference · 1 sampling family. Fish, basis not stated; Halibut, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 20 | 20 |
| Alternative weighting | 20 | 20 | 20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-halibut-fresh-fish-basis-not-stated:7dbbfeb0ad8d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bream and porgies (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Sea bream and porgies (fresh or raw) DMA reference · 1 sampling family. Fish, basis not stated; Sea bream and porgies, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 10 |
| Alternative weighting | 10 | 10 | 10 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-sea-bream-porgy-fresh-fish-basis-not-stated:294f256d984b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Croaker and drum (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Croaker and drum (fresh or raw) DMA reference · 1 sampling family. Fish, basis not stated; Croaker and drum, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 25 | 25 | 25 |
| Alternative weighting | 25 | 25 | 25 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-croaker-drum-fresh-fish-basis-not-stated:7060d3d885b0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hairtail and cutlassfish (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Hairtail and cutlassfish (fresh or raw) DMA reference · 1 sampling family. Fish, basis not stated; Hairtail and cutlassfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 13 | 25.5 | 38 |
| Alternative weighting | 13 | 25.5 | 38 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-hairtail-cutlassfish-fresh-fish-basis-not-stated:73b497d06914
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hairtail and cutlassfish (smoked, dried, salted or fermented) DMA reference · 1 sampling family
Reference and scope
HMI Hairtail and cutlassfish (smoked, dried, salted or fermented) DMA reference · 1 sampling family. Fish, basis not stated; Hairtail and cutlassfish, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 44 | 44 | 44 |
| Alternative weighting | 44 | 44 | 44 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-hairtail-cutlassfish-smoked-dried-salted-fermented-fish-basis-not-stated:9bb87dbe75eb
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Barracuda (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Barracuda (fresh or raw) DMA reference · 1 sampling family. Fish, basis not stated; Barracuda, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 10 |
| Alternative weighting | 10 | 10 | 10 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-barracuda-fresh-fish-basis-not-stated:42bf3c2f7b78
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other marine fish (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Other marine fish (fresh or raw) DMA reference · 1 sampling family. Fish, basis not stated; Other marine fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 40 | 50 | 70 |
| Alternative weighting | 40 | 50 | 70 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-other-marine-finfish-fresh-fish-basis-not-stated:ae08159c2a2f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (fresh or raw) DMA reference · 1 sampling family. Fish, wet weight; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10.5 | 5.51–20 (bounded) | 23.1 |
| Alternative weighting | ≤10.5 | 5.51–20 (bounded) | 23.1 |
7 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 7 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-fish-unspecified-marine-fresh-fish-wet-weight:a2e58abe342e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (fresh or raw) DMA reference · 1 sampling family. Fish, wet weight; Freshwater fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤15 | ≤20 |
| Alternative weighting | ≤10 | ≤15 | ≤20 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-fish-unspecified-freshwater-fresh-fish-wet-weight:802f83e3839a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) DMA reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (canned) DMA reference · 1 sampling family. Fish, wet weight; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤13 | 61.1–69.1 (bounded) |
| Alternative weighting | ≤10 | ≤13 | 61.1–69.1 (bounded) |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-fish-unspecified-canned-fish-wet-weight:9dcd175ee5d2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) DMA reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish product) DMA reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤20 | ≤20 |
| Alternative weighting | ≤20 | ≤20 | ≤20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-fish-unspecified-fish-product-fish-wet-weight:4ce423998868
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) DMA reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fresh or raw) DMA reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤7 | 3.5–13.5 (bounded) | 7–20 (bounded) |
| Alternative weighting | ≤7 | 3.5–13.5 (bounded) | 7–20 (bounded) |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-fish-unspecified-fresh-fish-wet-weight:915c51b3e517
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (smoked, dried, salted or fermented) DMA reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (smoked, dried, salted or fermented) DMA reference · 1 sampling family. Fish, wet weight; Fish, species not stated, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | 16.4 | 302 |
| Alternative weighting | ≤10 | 16.4 | 302 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-DMA-fish-unspecified-smoked-dried-salted-fermented-fish-wet-weight:c45a2309cbee
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) MMA reference · 1 sampling family
Reference and scope
HMI Mackerel (fresh or raw) MMA reference · 1 sampling family. Fish, basis not stated; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 63 | 81.5 | 100 |
| Alternative weighting | 63 | 81.5 | 100 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MMA-mackerel-fresh-fish-basis-not-stated:8ef365739d8f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) MMA reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (fresh or raw) MMA reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤13 | ≤13 | ≤13 |
| Alternative weighting | ≤13 | ≤13 | ≤13 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MMA-sardine-pilchard-fresh-fish-wet-weight:8459429e6203
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) MMA reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (fresh or raw) MMA reference · 1 sampling family. Fish, basis not stated; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 10 |
| Alternative weighting | 10 | 10 | 10 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MMA-sardine-pilchard-fresh-fish-basis-not-stated:219fa2a2883e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (fresh or raw) MMA reference · 1 sampling family
Reference and scope
HMI Anchovy (fresh or raw) MMA reference · 1 sampling family. Fish, basis not stated; Anchovy, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 50 | 50 | 50 |
| Alternative weighting | 50 | 50 | 50 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MMA-anchovy-fresh-fish-basis-not-stated:1f33b6b74b26
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) MMA reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) MMA reference · 1 sampling family. Fish, wet weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1.56 | ≤1.56 | ≤1.56 |
| Alternative weighting | ≤1.56 | ≤1.56 | ≤1.56 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MMA-trout-fresh-fish-wet-weight:4b901800a95c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Croaker and drum (fresh or raw) MMA reference · 1 sampling family
Reference and scope
HMI Croaker and drum (fresh or raw) MMA reference · 1 sampling family. Fish, basis not stated; Croaker and drum, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 83 | 83 | 83 |
| Alternative weighting | 83 | 83 | 83 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MMA-croaker-drum-fresh-fish-basis-not-stated:38db553a098f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hairtail and cutlassfish (fresh or raw) MMA reference · 1 sampling family
Reference and scope
HMI Hairtail and cutlassfish (fresh or raw) MMA reference · 1 sampling family. Fish, basis not stated; Hairtail and cutlassfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 67 | 75 | 83 |
| Alternative weighting | 67 | 75 | 83 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MMA-hairtail-cutlassfish-fresh-fish-basis-not-stated:c06931c6e2b6
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other marine fish (fresh or raw) MMA reference · 1 sampling family
Reference and scope
HMI Other marine fish (fresh or raw) MMA reference · 1 sampling family. Fish, basis not stated; Other marine fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 20 | 20 |
| Alternative weighting | 20 | 20 | 20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MMA-other-marine-finfish-fresh-fish-basis-not-stated:2c69553f222a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) MMA reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (fresh or raw) MMA reference · 1 sampling family. Fish, wet weight; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1.56 | ≤1.56 | ≤1.56 |
| Alternative weighting | ≤1.56 | ≤1.56 | ≤1.56 |
5 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 5 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MMA-fish-unspecified-marine-fresh-fish-wet-weight:8e1d688a6993
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) MMA reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (canned) MMA reference · 1 sampling family. Fish, wet weight; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1.94 | 0.972–7.47 (bounded) | 1.94–13 (bounded) |
| Alternative weighting | ≤1.94 | 0.972–7.47 (bounded) | 1.94–13 (bounded) |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MMA-fish-unspecified-canned-fish-wet-weight:441e403ac9af
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) MMA reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fresh or raw) MMA reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1.56 | ≤10.8 | ≤20 |
| Alternative weighting | ≤1.56 | ≤10.8 | ≤20 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MMA-fish-unspecified-fresh-fish-wet-weight:d91008774bf1
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (smoked, dried, salted or fermented) MMA reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (smoked, dried, salted or fermented) MMA reference · 1 sampling family. Fish, wet weight; Fish, species not stated, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 7.95 | 7.95 | 7.95 |
| Alternative weighting | 7.95 | 7.95 | 7.95 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-MMA-fish-unspecified-smoked-dried-salted-fermented-fish-wet-weight:0bae20d62e92
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Tuna (fresh or raw) oAs reference · 1 sampling family. Fish, wet weight; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 253 | 402 | 551 |
| Alternative weighting | 253 | 402 | 551 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-tuna-fresh-fish-wet-weight:4e0ff86ddce4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Tuna (fresh or raw) oAs reference · 1 sampling family. Fish, basis not stated; Tuna, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 50 | 140 |
| Alternative weighting | 10 | 50 | 140 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-tuna-fresh-fish-basis-not-stated:da03b75d915f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Mackerel (fresh or raw) oAs reference · 1 sampling family. Fish, wet weight; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 118 | 128 | 138 |
| Alternative weighting | 118 | 128 | 138 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-mackerel-fresh-fish-wet-weight:069fec5e2454
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Mackerel (fresh or raw) oAs reference · 1 sampling family. Fish, basis not stated; Mackerel, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 38.5 | 607 | 1470 |
| Alternative weighting | 38.5 | 607 | 1470 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-mackerel-fresh-fish-basis-not-stated:9730d350cd72
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Horse mackerel, jacks and trevally (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Horse mackerel, jacks and trevally (fresh or raw) oAs reference · 1 sampling family. Fish, basis not stated; Horse mackerel, jacks and trevally, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 20 | 620 |
| Alternative weighting | 20 | 20 | 620 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-horse-mackerel-jack-fresh-fish-basis-not-stated:962b58221348
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Herring (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Herring (fresh or raw) oAs reference · 1 sampling family. Fish, wet weight; Herring, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 109 | 179 | 248 |
| Alternative weighting | 109 | 179 | 248 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-herring-fresh-fish-wet-weight:0fd258d18f7e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (fresh or raw) oAs reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤20 | ≤20 |
| Alternative weighting | ≤20 | ≤20 | ≤20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-sardine-pilchard-fresh-fish-wet-weight:dff00dbcbf8c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (fresh or raw) oAs reference · 1 sampling family. Fish, basis not stated; Sardine and pilchard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 40 | 2060 | 4070 |
| Alternative weighting | 40 | 2060 | 4070 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-sardine-pilchard-fresh-fish-basis-not-stated:fe1d7fcc4f36
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Anchovy (fresh or raw) oAs reference · 1 sampling family. Fish, basis not stated; Anchovy, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 1010 | 2010 |
| Alternative weighting | 10 | 1010 | 2010 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-anchovy-fresh-fish-basis-not-stated:aa81fb3b19f2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shad, hilsa and other herrings (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Shad, hilsa and other herrings (fresh or raw) oAs reference · 1 sampling family. Fish, basis not stated; Shad, hilsa and other herrings, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 680 | 680 | 680 |
| Alternative weighting | 680 | 680 | 680 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-shad-other-clupeid-fresh-fish-basis-not-stated:6f9459e5788e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Salmon (fresh or raw) oAs reference · 1 sampling family. Fish, wet weight; Salmon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 62.9 | 66.5 | 70.1 |
| Alternative weighting | 62.9 | 66.5 | 70.1 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-salmon-fresh-fish-wet-weight:36cfdb7ed2d2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Trout and char (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Trout and char (fresh or raw) oAs reference · 1 sampling family. Fish, wet weight; Trout and char, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 110 | 110 | 110 |
| Alternative weighting | 110 | 110 | 110 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-trout-fresh-fish-wet-weight:bd6dbe2eadcc
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Cod (fresh or raw) oAs reference · 1 sampling family. Fish, wet weight; Cod, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 15–25 (bounded) | 176–181 (bounded) | 337 |
| Alternative weighting | 15–25 (bounded) | 176–181 (bounded) | 337 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-cod-fresh-fish-wet-weight:be6a135ebf38
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Plaice, flounder, sole and turbot (fresh or raw) oAs reference · 1 sampling family. Fish, basis not stated; Plaice, flounder, sole and turbot, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 40 | 130 | 910 |
| Alternative weighting | 40 | 130 | 910 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-plaice-flounder-sole-fresh-fish-basis-not-stated:644c579204e4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Halibut (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Halibut (fresh or raw) oAs reference · 1 sampling family. Fish, basis not stated; Halibut, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 785 | 1560 |
| Alternative weighting | 10 | 785 | 1560 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-halibut-fresh-fish-basis-not-stated:508c0b9ab639
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bream and porgies (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Sea bream and porgies (fresh or raw) oAs reference · 1 sampling family. Fish, basis not stated; Sea bream and porgies, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 450 | 880 |
| Alternative weighting | 20 | 450 | 880 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-sea-bream-porgy-fresh-fish-basis-not-stated:96b10fa63b7e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Croaker and drum (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Croaker and drum (fresh or raw) oAs reference · 1 sampling family. Fish, basis not stated; Croaker and drum, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 25 | 123 | 220 |
| Alternative weighting | 25 | 123 | 220 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-croaker-drum-fresh-fish-basis-not-stated:0ddd74f35ba7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Croaker and drum (smoked, dried, salted or fermented) oAs reference · 1 sampling family
Reference and scope
HMI Croaker and drum (smoked, dried, salted or fermented) oAs reference · 1 sampling family. Fish, basis not stated; Croaker and drum, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 38 | 834 | 1630 |
| Alternative weighting | 38 | 834 | 1630 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-croaker-drum-smoked-dried-salted-fermented-fish-basis-not-stated:3523ee64b334
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Emperors and grunts (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Emperors and grunts (fresh or raw) oAs reference · 1 sampling family. Fish, basis not stated; Emperors and grunts, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 60 | 280 | 500 |
| Alternative weighting | 60 | 280 | 500 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-emperor-grunt-fresh-fish-basis-not-stated:52df55889f5b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hairtail and cutlassfish (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Hairtail and cutlassfish (fresh or raw) oAs reference · 1 sampling family. Fish, basis not stated; Hairtail and cutlassfish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 34.5 | 110 | 400 |
| Alternative weighting | 34.5 | 110 | 400 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-hairtail-cutlassfish-fresh-fish-basis-not-stated:dd9825dd7119
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Hairtail and cutlassfish (smoked, dried, salted or fermented) oAs reference · 1 sampling family
Reference and scope
HMI Hairtail and cutlassfish (smoked, dried, salted or fermented) oAs reference · 1 sampling family. Fish, basis not stated; Hairtail and cutlassfish, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 19 | 1650 | 3290 |
| Alternative weighting | 19 | 1650 | 3290 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Park et al. 2005 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-hairtail-cutlassfish-smoked-dried-salted-fermented-fish-basis-not-stated:bef565dfc961
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Barracuda (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Barracuda (fresh or raw) oAs reference · 1 sampling family. Fish, basis not stated; Barracuda, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 40 | 60 | 700 |
| Alternative weighting | 40 | 60 | 700 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-barracuda-fresh-fish-basis-not-stated:53da1542da78
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Other marine fish (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Other marine fish (fresh or raw) oAs reference · 1 sampling family. Fish, basis not stated; Other marine fish, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 40 | 200 | 510 |
| Alternative weighting | 30 | 140 | 510 |
11 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Kaise et al. 1988 | 11 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-other-marine-finfish-fresh-fish-basis-not-stated:98b1a55c2cc4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (fresh or raw) oAs reference · 1 sampling family. Fish, wet weight; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20–30 (bounded) | 1090 | 3510 |
| Alternative weighting | 20–30 (bounded) | 1090 | 3510 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-fish-unspecified-marine-fresh-fish-wet-weight:8047ba296b02
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (fresh or raw) oAs reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (fresh or raw) oAs reference · 1 sampling family. Fish, wet weight; Freshwater fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | 86.1–96.1 (bounded) | 172 |
| Alternative weighting | ≤20 | 86.1–96.1 (bounded) | 172 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-fish-unspecified-freshwater-fresh-fish-wet-weight:23a066c05556
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) oAs reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (canned) oAs reference · 1 sampling family. Fish, wet weight; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 170 | 170 | 170 |
| Alternative weighting | 170 | 170 | 170 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-fish-unspecified-canned-fish-wet-weight:db13edab67b8
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) oAs reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish product) oAs reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤20 | ≤20 |
| Alternative weighting | ≤20 | ≤20 | ≤20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-oAs-fish-unspecified-fish-product-fish-wet-weight:c506dc3fd063
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (fresh or raw) As_unspecified reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (fresh or raw) As_unspecified reference · 1 sampling family. Fish, basis not stated; Carp and other cyprinids, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 33.7 | 47.5 | 59.2 |
| Alternative weighting | 33.7 | 47.5 | 59.2 |
10 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Najem et al. 2024 | 10 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-As_unspecified-carp-cyprinid-fresh-fish-basis-not-stated:87a57fd2a529
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (canned) Ni reference · 2 sampling families
Reference and scope
HMI Tuna (canned) Ni reference · 2 sampling families. Fish, wet weight; Tuna, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1.11 | ≤20.6 | ≤40 |
| Alternative weighting | ≤1.11 | ≤20.6 | ≤40 |
9 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 50% |
| De et al. 2021 | 8 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-tuna-canned-fish-wet-weight:9a33005a9c88
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (canned) Ni reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (canned) Ni reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1.11 | ≤1.11 | ≤1.11 |
| Alternative weighting | ≤1.11 | ≤1.11 | ≤1.11 |
10 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| De et al. 2021 | 10 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-sardine-pilchard-canned-fish-wet-weight:445b4e6c8577
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (canned) Ni reference · 1 sampling family
Reference and scope
HMI Salmon (canned) Ni reference · 1 sampling family. Fish, wet weight; Salmon, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤20 | ≤20 |
| Alternative weighting | ≤20 | ≤20 | ≤20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-salmon-canned-fish-wet-weight:b744c0e41904
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (cooked) Ni reference · 1 sampling family
Reference and scope
HMI Salmon (cooked) Ni reference · 1 sampling family. Fish, wet weight; Salmon, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤40 | ≤40 | ≤40 |
| Alternative weighting | ≤40 | ≤40 | ≤40 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-salmon-cooked-fish-wet-weight:fb964f0a5f18
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (cooked) Ni reference · 1 sampling family
Reference and scope
HMI Cod (cooked) Ni reference · 1 sampling family. Fish, wet weight; Cod, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤40 | ≤40 | ≤40 |
| Alternative weighting | ≤40 | ≤40 | ≤40 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-cod-cooked-fish-wet-weight:86167fa4bb27
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bream and porgies (fresh or raw) Ni reference · 1 sampling family
Reference and scope
HMI Sea bream and porgies (fresh or raw) Ni reference · 1 sampling family. Fish, wet weight; Sea bream and porgies, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1 | 3 | 16 |
| Alternative weighting | 1 | 3 | 16 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-sea-bream-porgy-fresh-fish-wet-weight:a0347d2a61e3
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Barracuda (fresh or raw) Ni reference · 1 sampling family
Reference and scope
HMI Barracuda (fresh or raw) Ni reference · 1 sampling family. Fish, wet weight; Barracuda, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 3 | 3 | 3 |
| Alternative weighting | 3 | 3 | 3 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-barracuda-fresh-fish-wet-weight:ce7747bfc32f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Gurnard (fresh or raw) Ni reference · 1 sampling family
Reference and scope
HMI Gurnard (fresh or raw) Ni reference · 1 sampling family. Fish, wet weight; Gurnard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2 | 2 | 2 |
| Alternative weighting | 2 | 2 | 2 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-gurnard-fresh-fish-wet-weight:62d4fe959996
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tilapia (cooked) Ni reference · 1 sampling family
Reference and scope
HMI Tilapia (cooked) Ni reference · 1 sampling family. Fish, wet weight; Tilapia, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤40 | ≤40 | ≤40 |
| Alternative weighting | ≤40 | ≤40 | ≤40 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-tilapia-cooked-fish-wet-weight:4283656efa4a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Marine fish, species not stated (fresh or raw) Ni reference · 1 sampling family
Reference and scope
HMI Marine fish, species not stated (fresh or raw) Ni reference · 1 sampling family. Fish, basis not stated; Marine fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 7 | 7 | 7 |
| Alternative weighting | 7 | 7 | 7 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Han et al. 2024 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-fish-unspecified-marine-fresh-fish-basis-not-stated:bcc6d6da6b51
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Freshwater fish, species not stated (fresh or raw) Ni reference · 1 sampling family
Reference and scope
HMI Freshwater fish, species not stated (fresh or raw) Ni reference · 1 sampling family. Fish, basis not stated; Freshwater fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 10 |
| Alternative weighting | 10 | 10 | 10 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Han et al. 2024 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-fish-unspecified-freshwater-fresh-fish-basis-not-stated:58ae5774bde1
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) Ni reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (canned) Ni reference · 1 sampling family. Fish, wet weight; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤20 | ≤20 |
| Alternative weighting | ≤20 | ≤20 | ≤20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-fish-unspecified-canned-fish-wet-weight:ccd40dfe8ac4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) Ni reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (canned) Ni reference · 2 sampling families. Fish, basis not stated; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 101 | 204 | 204 |
| Alternative weighting | 101 | 204 | 204 |
6 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Dabeka et al. 1995 | 5 | 50% |
| Han et al. 2024 | 1 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-fish-unspecified-canned-fish-basis-not-stated:f8824e632819
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (cooked) Ni reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (cooked) Ni reference · 1 sampling family. Fish, wet weight; Fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 120 | 175 | 230 |
| Alternative weighting | 120 | 175 | 230 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-fish-unspecified-cooked-fish-wet-weight:98b71aa40425
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) Ni reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (fish product) Ni reference · 2 sampling families. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 85 | 100 | 110 |
| Alternative weighting | 85 | 100 | 110 |
3 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 50% |
| Baxter et al. 2015 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-fish-unspecified-fish-product-fish-wet-weight:c6a826943e47
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (smoked, dried, salted or fermented) Ni reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (smoked, dried, salted or fermented) Ni reference · 1 sampling family. Fish, basis not stated; Fish, species not stated, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 3890 | 4050 | 4170 |
| Alternative weighting | 3890 | 4050 | 4170 |
5 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Bazie et al. 2022 | 5 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Ni-fish-unspecified-smoked-dried-salted-fermented-fish-basis-not-stated:eb555c1c32b9
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (canned) Cr reference · 2 sampling families
Reference and scope
HMI Tuna (canned) Cr reference · 2 sampling families. Fish, wet weight; Tuna, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤0.809 | ≤25.4 | ≤50 |
| Alternative weighting | ≤0.809 | ≤25.4 | ≤50 |
9 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 50% |
| De et al. 2021 | 8 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cr-tuna-canned-fish-wet-weight:e790f84dab07
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shark (fresh or raw) Cr reference · 1 sampling family
Reference and scope
HMI Shark (fresh or raw) Cr reference · 1 sampling family. Fish, wet weight; Shark, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤0.1 | 11 | 125 |
| Alternative weighting | ≤0.1 | 11 | 125 |
25 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Sang et al. 2019 | 25 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cr-shark-fresh-fish-wet-weight:8520c0f53559
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (canned) Cr reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (canned) Cr reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 12 | 17 | 26 |
| Alternative weighting | 12 | 17 | 26 |
10 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| De et al. 2021 | 10 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cr-sardine-pilchard-canned-fish-wet-weight:f928d109e695
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (canned) Cr reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (canned) Cr reference · 1 sampling family. Fish, basis not stated; Sardine and pilchard, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 180 | 180 | 180 |
| Alternative weighting | 180 | 180 | 180 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Evaluation of… 2025 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cr-sardine-pilchard-canned-fish-basis-not-stated:c908d2bcead0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (canned) Cr reference · 1 sampling family
Reference and scope
HMI Salmon (canned) Cr reference · 1 sampling family. Fish, wet weight; Salmon, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤20 | ≤20 |
| Alternative weighting | ≤20 | ≤20 | ≤20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cr-salmon-canned-fish-wet-weight:d76ddc7d2a07
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (cooked) Cr reference · 1 sampling family
Reference and scope
HMI Salmon (cooked) Cr reference · 1 sampling family. Fish, wet weight; Salmon, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤50 | ≤50 | ≤50 |
| Alternative weighting | ≤50 | ≤50 | ≤50 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cr-salmon-cooked-fish-wet-weight:52faeb7922db
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (cooked) Cr reference · 1 sampling family
Reference and scope
HMI Cod (cooked) Cr reference · 1 sampling family. Fish, wet weight; Cod, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤50 | ≤50 | ≤50 |
| Alternative weighting | ≤50 | ≤50 | ≤50 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cr-cod-cooked-fish-wet-weight:5e760c911c5f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sea bream and porgies (fresh or raw) Cr reference · 1 sampling family
Reference and scope
HMI Sea bream and porgies (fresh or raw) Cr reference · 1 sampling family. Fish, wet weight; Sea bream and porgies, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 40 |
| Alternative weighting | 10 | 10 | 40 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cr-sea-bream-porgy-fresh-fish-wet-weight:3e38f8d01cbe
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Barracuda (fresh or raw) Cr reference · 1 sampling family
Reference and scope
HMI Barracuda (fresh or raw) Cr reference · 1 sampling family. Fish, wet weight; Barracuda, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 10 |
| Alternative weighting | 10 | 10 | 10 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cr-barracuda-fresh-fish-wet-weight:8c26ca30e906
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Gurnard (fresh or raw) Cr reference · 1 sampling family
Reference and scope
HMI Gurnard (fresh or raw) Cr reference · 1 sampling family. Fish, wet weight; Gurnard, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 20 | 20 |
| Alternative weighting | 20 | 20 | 20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Di et al. 2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cr-gurnard-fresh-fish-wet-weight:dede998b0fa7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tilapia (cooked) Cr reference · 1 sampling family
Reference and scope
HMI Tilapia (cooked) Cr reference · 1 sampling family. Fish, wet weight; Tilapia, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤50 | ≤50 | ≤50 |
| Alternative weighting | ≤50 | ≤50 | ≤50 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cr-tilapia-cooked-fish-wet-weight:d3ba7964d5fb
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) Cr reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (canned) Cr reference · 1 sampling family. Fish, wet weight; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤20 | ≤20 |
| Alternative weighting | ≤20 | ≤20 | ≤20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cr-fish-unspecified-canned-fish-wet-weight:704b52e0b6f5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (cooked) Cr reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (cooked) Cr reference · 1 sampling family. Fish, wet weight; Fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | 20–30 (bounded) | 40 |
| Alternative weighting | ≤20 | 20–30 (bounded) | 40 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cr-fish-unspecified-cooked-fish-wet-weight:f39189af0122
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) Cr reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (fish product) Cr reference · 2 sampling families. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 65 | 135 | 200 |
| Alternative weighting | 65 | 135 | 200 |
3 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 50% |
| Baxter et al. 2015 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cr-fish-unspecified-fish-product-fish-wet-weight:be2eecb2a07d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (smoked, dried, salted or fermented) Cr reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (smoked, dried, salted or fermented) Cr reference · 1 sampling family. Fish, basis not stated; Fish, species not stated, smoked, dried, salted or fermented; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1830 | 1870 | 1870 |
| Alternative weighting | 1830 | 1870 | 1870 |
5 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Bazie et al. 2022 | 5 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Cr-fish-unspecified-smoked-dried-salted-fermented-fish-basis-not-stated:5d317e3abb26
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (canned) Al reference · 1 sampling family
Reference and scope
HMI Tuna (canned) Al reference · 1 sampling family. Fish, wet weight; Tuna, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤4.43 | 5130 | 19100 |
| Alternative weighting | ≤4.43 | 5130 | 19100 |
16 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| De et al. 2021 | 16 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Al-tuna-canned-fish-wet-weight:7a4326dc8fd8
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (cooked) Al reference · 1 sampling family
Reference and scope
HMI Tuna (cooked) Al reference · 1 sampling family. Fish, wet weight; Tuna, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤236 | 755–932 (bounded) | 1510–1630 (bounded) |
| Alternative weighting | ≤236 | 755–932 (bounded) | 1510–1630 (bounded) |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Al-tuna-cooked-fish-wet-weight:702c717ad41b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (canned) Al reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (canned) Al reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 13 | 20.5 | 28 |
| Alternative weighting | 13 | 20.5 | 28 |
10 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| De et al. 2021 | 10 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Al-sardine-pilchard-canned-fish-wet-weight:f0f96f359169
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (canned) Al reference · 1 sampling family
Reference and scope
HMI Salmon (canned) Al reference · 1 sampling family. Fish, wet weight; Salmon, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2880 | 2880 | 2880 |
| Alternative weighting | 2880 | 2880 | 2880 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Al-salmon-canned-fish-wet-weight:bc2a21abe06c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (cooked) Al reference · 1 sampling family
Reference and scope
HMI Salmon (cooked) Al reference · 1 sampling family. Fish, wet weight; Salmon, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 268–386 (bounded) | 495–613 (bounded) | 595–713 (bounded) |
| Alternative weighting | 268–386 (bounded) | 495–613 (bounded) | 595–713 (bounded) |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Al-salmon-cooked-fish-wet-weight:7d83fc30aee1
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) Al reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (canned) Al reference · 1 sampling family. Fish, wet weight; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 390 | 390 | 390 |
| Alternative weighting | 390 | 390 | 390 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Al-fish-unspecified-canned-fish-wet-weight:60ce9ab35443
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (cooked) Al reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (cooked) Al reference · 2 sampling families. Fish, wet weight; Fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 100–105 (bounded) | 110–173 (bounded) | 491–609 (bounded) |
| Alternative weighting | 100–105 (bounded) | 110–173 (bounded) | 491–609 (bounded) |
5 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 50% |
| Baxter et al. 2015 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Al-fish-unspecified-cooked-fish-wet-weight:613582b25bd7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) Al reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish product) Al reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1030 | 1390 | 1740 |
| Alternative weighting | 1030 | 1390 | 1740 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Al-fish-unspecified-fish-product-fish-wet-weight:ac8bc4828a35
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish sauce) Al reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish sauce) Al reference · 1 sampling family. Fish, basis not stated; Fish, species not stated, fish sauce; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 4100 | 5660 | 36400 |
| Alternative weighting | 4100 | 5660 | 36400 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Abdullah 2009 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Al-fish-unspecified-fish-sauce-fish-basis-not-stated:c6badeea8918
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (canned) Sn reference · 1 sampling family
Reference and scope
HMI Tuna (canned) Sn reference · 1 sampling family. Fish, wet weight; Tuna, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1 | 1 | 24 |
| Alternative weighting | 1 | 1 | 24 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-tuna-canned-fish-wet-weight:3c65a437e188
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (cooked) Sn reference · 1 sampling family
Reference and scope
HMI Tuna (cooked) Sn reference · 1 sampling family. Fish, wet weight; Tuna, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | 18.3–23.3 (bounded) | 71.8 |
| Alternative weighting | ≤10 | 18.3–23.3 (bounded) | 71.8 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 4 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-tuna-cooked-fish-wet-weight:ecbd6e75e174
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shark (fresh or raw) Sn reference · 1 sampling family
Reference and scope
HMI Shark (fresh or raw) Sn reference · 1 sampling family. Fish, wet weight; Shark, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤0.1 | ≤0.1 | 31.4 |
| Alternative weighting | ≤0.1 | ≤0.1 | 31.4 |
25 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Sang et al. 2019 | 25 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-shark-fresh-fish-wet-weight:da4bc71169ff
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Mackerel (canned) Sn reference · 1 sampling family
Reference and scope
HMI Mackerel (canned) Sn reference · 1 sampling family. Fish, wet weight; Mackerel, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1 | 1 | 1 |
| Alternative weighting | 1 | 1 | 1 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-mackerel-canned-fish-wet-weight:badcfc59aa80
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Sardine and pilchard (canned) Sn reference · 1 sampling family
Reference and scope
HMI Sardine and pilchard (canned) Sn reference · 1 sampling family. Fish, wet weight; Sardine and pilchard, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1 | 4 | 7 |
| Alternative weighting | 1 | 4 | 7 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-sardine-pilchard-canned-fish-wet-weight:c6dac842f9de
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Anchovy (canned) Sn reference · 1 sampling family
Reference and scope
HMI Anchovy (canned) Sn reference · 1 sampling family. Fish, wet weight; Anchovy, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1 | 1 | 1 |
| Alternative weighting | 1 | 1 | 1 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Olmedo et al. 2013 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-anchovy-canned-fish-wet-weight:7328ea98531e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (canned) Sn reference · 1 sampling family
Reference and scope
HMI Salmon (canned) Sn reference · 1 sampling family. Fish, wet weight; Salmon, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 40 | 40 | 40 |
| Alternative weighting | 40 | 40 | 40 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-salmon-canned-fish-wet-weight:4a7b491413f0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (cooked) Sn reference · 1 sampling family
Reference and scope
HMI Salmon (cooked) Sn reference · 1 sampling family. Fish, wet weight; Salmon, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2.14–2.89 (bounded) | 11.1 | 11.4 |
| Alternative weighting | 2.14–2.89 (bounded) | 11.1 | 11.4 |
3 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-salmon-cooked-fish-wet-weight:780ee517365a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (fresh or raw) Sn reference · 1 sampling family
Reference and scope
HMI Salmon (fresh or raw) Sn reference · 1 sampling family. Fish, wet weight; Salmon, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 100–130 (bounded) | 100–130 (bounded) | 100–130 (bounded) |
| Alternative weighting | 100–130 (bounded) | 100–130 (bounded) | 100–130 (bounded) |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-salmon-fresh-fish-wet-weight:706f29c3d1ad
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Plaice, flounder, sole and turbot (cooked) Sn reference · 1 sampling family
Reference and scope
HMI Plaice, flounder, sole and turbot (cooked) Sn reference · 1 sampling family. Fish, wet weight; Plaice, flounder, sole and turbot, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤10 | ≤10 |
| Alternative weighting | ≤10 | ≤10 | ≤10 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-plaice-flounder-sole-cooked-fish-wet-weight:7c6bf40b794a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Carp and other cyprinids (cooked) Sn reference · 1 sampling family
Reference and scope
HMI Carp and other cyprinids (cooked) Sn reference · 1 sampling family. Fish, wet weight; Carp and other cyprinids, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤10 | ≤10 |
| Alternative weighting | ≤10 | ≤10 | ≤10 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-carp-cyprinid-cooked-fish-wet-weight:a737112f0188
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Bream (species group not stated) (cooked) Sn reference · 1 sampling family
Reference and scope
HMI Bream (species group not stated) (cooked) Sn reference · 1 sampling family. Fish, wet weight; Bream (species group not stated), cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 25 | 25 | 25 |
| Alternative weighting | 25 | 25 | 25 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-bream-unspecified-cooked-fish-wet-weight:dc7a8e206703
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) Sn reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (canned) Sn reference · 1 sampling family. Fish, wet weight; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 50 | 50 | 50 |
| Alternative weighting | 50 | 50 | 50 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-fish-unspecified-canned-fish-wet-weight:f2f6913e6c75
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) Sn reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (canned) Sn reference · 1 sampling family. Fish, dry weight; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 20 | 20 |
| Alternative weighting | 20 | 20 | 20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Ye et al. 2026 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-fish-unspecified-canned-fish-dry-weight:4216499fee41
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (cooked) Sn reference · 2 sampling families
Reference and scope
HMI Fish, species not stated (cooked) Sn reference · 2 sampling families. Fish, wet weight; Fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | 4–10.5 (bounded) | 17 |
| Alternative weighting | ≤10 | 4–10.5 (bounded) | 17 |
7 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 5 | 50% |
| Baxter et al. 2015 | 2 | 50% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-fish-unspecified-cooked-fish-wet-weight:5bfde85833e7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) Sn reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish product) Sn reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | 5–10 (bounded) | 10 |
| Alternative weighting | ≤10 | 5–10 (bounded) | 10 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-fish-unspecified-fish-product-fish-wet-weight:1a5d4a71a3a2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) Sn reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fresh or raw) Sn reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 20 | 110 | 200 |
| Alternative weighting | 20 | 110 | 200 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-fish-unspecified-fresh-fish-wet-weight:482463e8d602
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fresh or raw) Sn reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fresh or raw) Sn reference · 1 sampling family. Fish, dry weight; Fish, species not stated, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 10 | 10 | 10 |
| Alternative weighting | 10 | 10 | 10 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Ye et al. 2026 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sn-fish-unspecified-fresh-fish-dry-weight:cb3e6c11ab66
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tuna (canned) U reference · 1 sampling family
Reference and scope
HMI Tuna (canned) U reference · 1 sampling family. Fish, wet weight; Tuna, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1 | ≤1 | ≤1 |
| Alternative weighting | ≤1 | ≤1 | ≤1 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-U-tuna-canned-fish-wet-weight:8f6a5de4d4ed
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (cooked) U reference · 1 sampling family
Reference and scope
HMI Salmon (cooked) U reference · 1 sampling family. Fish, wet weight; Salmon, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1 | ≤1 | ≤1 |
| Alternative weighting | ≤1 | ≤1 | ≤1 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-U-salmon-cooked-fish-wet-weight:d5fe539dab35
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Cod (cooked) U reference · 1 sampling family
Reference and scope
HMI Cod (cooked) U reference · 1 sampling family. Fish, wet weight; Cod, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1 | ≤1 | ≤1 |
| Alternative weighting | ≤1 | ≤1 | ≤1 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-U-cod-cooked-fish-wet-weight:76797c497ef7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Tilapia (cooked) U reference · 1 sampling family
Reference and scope
HMI Tilapia (cooked) U reference · 1 sampling family. Fish, wet weight; Tilapia, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1 | ≤1 | ≤1 |
| Alternative weighting | ≤1 | ≤1 | ≤1 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-U-tilapia-cooked-fish-wet-weight:182052d7d789
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) U reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish product) U reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1.1 | 1.1 | 1.1 |
| Alternative weighting | 1.1 | 1.1 | 1.1 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| FDA TDS FY2018–FY2020 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-U-fish-unspecified-fish-product-fish-wet-weight:bc4301d6c6e4
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Shark (fresh or raw) Sb reference · 1 sampling family
Reference and scope
HMI Shark (fresh or raw) Sb reference · 1 sampling family. Fish, wet weight; Shark, fresh or raw; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤0.1 | ≤0.1 | ≤0.1 |
| Alternative weighting | ≤0.1 | ≤0.1 | ≤0.1 |
25 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Sang et al. 2019 | 25 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sb-shark-fresh-fish-wet-weight:f147747d49cd
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Salmon (canned) Sb reference · 1 sampling family
Reference and scope
HMI Salmon (canned) Sb reference · 1 sampling family. Fish, wet weight; Salmon, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 18.5 | 18.5 | 18.5 |
| Alternative weighting | 18.5 | 18.5 | 18.5 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sb-salmon-canned-fish-wet-weight:7cb69d6a5432
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (canned) Sb reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (canned) Sb reference · 1 sampling family. Fish, wet weight; Fish, species not stated, canned; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1.6 | 1.6 | 1.6 |
| Alternative weighting | 1.6 | 1.6 | 1.6 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 1 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sb-fish-unspecified-canned-fish-wet-weight:d92856186ea8
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (cooked) Sb reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (cooked) Sb reference · 1 sampling family. Fish, wet weight; Fish, species not stated, cooked; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤0.5 | 1.1–1.35 (bounded) | 2.2 |
| Alternative weighting | ≤0.5 | 1.1–1.35 (bounded) | 2.2 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sb-fish-unspecified-cooked-fish-wet-weight:e07c39efabac
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI Fish, species not stated (fish product) Sb reference · 1 sampling family
Reference and scope
HMI Fish, species not stated (fish product) Sb reference · 1 sampling family. Fish, wet weight; Fish, species not stated, fish product; µg/kg. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2.3 | 2.6 | 2.9 |
| Alternative weighting | 2.3 | 2.6 | 2.9 |
2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Baxter et al. 2015 | 2 | 100% |
Methods
HMI pools subgroup medians for one fish species group, one preparation form, one analyte species and one basis from every compatible sampling family in the evidence ledger: WHO GEMS/Food region-by-year medians (random sampling only), FDA Total Diet Study composites, per-fish or per-sample values printed by individual studies, and published subgroup medians. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference, not a probability sample of any fish market. A species group can contain several species with different mercury levels; GEMS/Food regions are reporting regions, not catch or farm origins. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:fish-Sb-fish-unspecified-fish-product-fish-wet-weight:b2b155c05ff5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
The source reports only a percentile, range or maximum for these samples, with no mean or median to place against the reference. Spread figures that do have a mean or median are shown on that row instead.
The value could not be reconciled with its own paper, so it is shown but not compared.
The result is below a reporting limit, and the range from zero to that limit crosses more than one band.
No medians or sample values exist for this form and metal, so no HMI reference could be built.
The HMI reference for this form has fewer than four units or no measurable spread, below the display minimum.
The result is on a basis (dry weight, or not stated) that no HMI reference for this form uses, so it cannot be placed.
Reporting limits overlap the study comparison, so no direction can be shown.
No findings match these filters. Change the selection or reset to show all source findings.
How metals reach fish
Methylmercury builds up through the food web, so fish that are older, larger and higher in the food chain carry more of it.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source →23Evaluation of Certain Food Additives and Contaminants (Methylmercury), 61st Meeting of JECFAWHO Technical Report Series 922Read source → Within one species the same pattern holds: modelled mean mercury in northern pike from Great Slave Lake was 740 µg/kg in fish of 600 mm or longer against 300 µg/kg in smaller fish, and young yellowtail in Japanese markets averaged 80 µg/kg total mercury against 520 µg/kg in adults.5Assessing mercury exposure to water and fish of the Mackenzie watershed using a Bayesian network analysisIntegrated Environmental Assessment and ManagementRead source →10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source → Large wild bluefin tuna caught off Sardinia averaged 1,680 µg/kg total mercury, against 610 µg/kg in bluefin fattened on a Maltese farm.24Bluefin Tuna (Thunnus thynnus L.) MusclePeer-reviewed articleRead source →
Cadmium, lead and inorganic arsenic in fish come mainly from the water, sediment and feed of the place where the fish lived, rather than building up with age along the food chain as methylmercury does.7Heavy Metal Levels and Cancer Risk Assessments of the Commercial Denis, Sparus aurata Collected from Bardawil Lake and Private Fish Farm Waters as a Cultured Source, EgyptNot reportedRead source →12Scientific Opinion of the Panel on Contaminants in the Food Chain on a request from the European Commission on cadmium in foodThe EFSA JournalRead source →25Scientific Opinion on Lead in FoodEFSA Journal 2010;8(4):1570Read source → This is why the higher muscle values cluster in studies from polluted rivers, lagoons and coastal sites, while large national monitoring programmes report low medians.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →7Heavy Metal Levels and Cancer Risk Assessments of the Commercial Denis, Sparus aurata Collected from Bardawil Lake and Private Fish Farm Waters as a Cultured Source, EgyptNot reportedRead source →12Scientific Opinion of the Panel on Contaminants in the Food Chain on a request from the European Commission on cadmium in foodThe EFSA JournalRead source →
Arsenic follows a different route: arsenobetaine, an organic compound, is the major form of arsenic in fish, which is why total arsenic can be high while inorganic arsenic stays low.4Dietary exposure to inorganic arsenic in the European populationEFSA Journal 2014;12(3):3597Read source →26Risk assessment of small organoarsenic species in foodEFSA JournalRead source → In UK samples analysed by two procedures, herring had 1,100 µg/kg total arsenic and 20–40 µg/kg inorganic arsenic, and haddock 2,600 µg/kg total against 20 µg/kg inorganic.22Determination of Total Inorganic Arsenic in Fish, Shellfish and Fish ProductsAnalystRead source →
Which species and sources measured lower
For mercury, species is the strongest and most consistent lower-contamination lever.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source →2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source → In EFSA’s European data the lowest mean total mercury among commonly eaten fish was in salmon and trout (31–35 µg/kg), sardine and pilchard (32–44 µg/kg) and herring (36 µg/kg), with carp (55 µg/kg) and anchovy (73–92 µg/kg) also low; the highest were swordfish, shark, pike (394 µg/kg) and tuna.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source → Hong Kong’s total diet study gave the same picture for methylmercury in local fish as eaten, from 4.5 µg/kg in grass carp and 7.9 µg/kg in sole to 330 µg/kg in tuna.27The First Hong Kong Total Diet Study: Metallic ContaminantsCentre for Food Safety, Food and Environmental Hygiene Department, Government of the Hong Kong Special Administrative RegionRead source → Because these rankings recur across European, Asian and US datasets with different methods, choosing small, short-lived and plankton-eating species is a supported preference for lower mercury, not just a single-study observation.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source →3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →8Advice About Eating Fish — For Those Who Might Become or Are Pregnant or Breastfeeding and Children Ages 1 to 11 YearsU.S. FDA and U.S. EPARead source →27The First Hong Kong Total Diet Study: Metallic ContaminantsCentre for Food Safety, Food and Environmental Hygiene Department, Government of the Hong Kong Special Administrative RegionRead source →
Within a species, farming and size can matter as much as origin. Farmed Atlantic salmon from Norway averaged 18 µg/kg total mercury against 56 µg/kg in wild salmon from the same coast, and farmed bluefin tuna and yellowtail in Japanese retail were lower than wild fish (530 against 760 µg/kg, and 130 against 520 µg/kg).6PCBs and Heavy Metals in Farmed, Escaped and WildPeer-reviewed articleRead source →10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source → Arsenic did not follow mercury: the same Norwegian study found 860 µg/kg arsenic in farmed salmon against 2,560 µg/kg in wild, while a US comparison of coho salmon found more total arsenic in the farmed fish (597 against 354 µg/kg, one sample each).6PCBs and Heavy Metals in Farmed, Escaped and WildPeer-reviewed articleRead source →28Determination of total arsenic and hydrophilic arsenic species in seafoodJournal of Food Composition and AnalysisRead source → These are within-study observations for particular farms and fisheries; they support asking for species, size and farm or catch origin, not a general rule that farmed fish are always lower.
Origin comparisons for the same species are weaker than species comparisons. Canned tuna bought in 36 countries had country means from 20 to 950 µg/kg total mercury, with both the lowest and some of the highest means from skipjack-labelled cans; only three cans were tested per country, and purchase country was not catch area.29Determination of toxic metals in canned tuna sold in developed and developing countries: Health risk assessment associated with human consumptionMarine Pollution BulletinRead source → For cadmium and lead the lowest monitored medians come from routine national programmes such as GEMS/Food in Europe, where most cod, trout and salmon results were below detection, rather than from any single producing region.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source → For inorganic arsenic, European fish means ranged from 0.7 µg/kg in herring to 20 µg/kg in sardine at the lower bound, so species differences are small compared with the EU limits of 100 and 500 µg/kg.4Dietary exposure to inorganic arsenic in the European populationEFSA Journal 2014;12(3):3597Read source →16Commission Regulation (EU) 2025/1891 of 17 September 2025 amending Regulation (EU) 2023/915 as regards maximum levels of inorganic arsenic in fish and other seafoodOfficial Journal of the European UnionRead source → Total arsenic, mostly organic, is far lower in freshwater fish: GEMS/Food European medians were about 55–75 µg/kg for freshwater fish against 3,100 µg/kg for marine fish, and US baked tilapia had 100 µg/kg against 4,500 µg/kg in baked cod.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →
Which fish are lowest in mercury?
Across European monitoring data, salmon and trout (31–35 µg/kg), sardine and pilchard (32–44 µg/kg), herring (36 µg/kg) and carp (55 µg/kg) had the lowest mean total mercury among commonly eaten fish.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source → US Total Diet Study tilapia had a median of 5.1 µg/kg and salmon 18 µg/kg, and GEMS/Food European medians were 18–30 µg/kg for sardine and 23–29 µg/kg for trout.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source → These are species averages; individual large or old fish can be much higher.5Assessing mercury exposure to water and fish of the Mackenzie watershed using a Bayesian network analysisIntegrated Environmental Assessment and ManagementRead source →
Is farmed fish lower in metals than wild fish?
For mercury, the measured comparisons found farmed fish lower: Norwegian farmed salmon 18 against 56 µg/kg wild, and Japanese farmed yellowtail 130 against 520 µg/kg.6PCBs and Heavy Metals in Farmed, Escaped and WildPeer-reviewed articleRead source →10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source → For arsenic the result was mixed, lower in farmed salmon in Norway but higher in a US farmed coho sample.6PCBs and Heavy Metals in Farmed, Escaped and WildPeer-reviewed articleRead source →28Determination of total arsenic and hydrophilic arsenic species in seafoodJournal of Food Composition and AnalysisRead source → Farm siting and feed can raise cadmium and lead where water is polluted, as in some Egyptian farms and lagoons.7Heavy Metal Levels and Cancer Risk Assessments of the Commercial Denis, Sparus aurata Collected from Bardawil Lake and Private Fish Farm Waters as a Cultured Source, EgyptNot reportedRead source →
Cooking, canning and other processing
Cooking does not remove mercury from fish; it concentrates it as water is lost.30Iodine and Mercury Content in Raw, Boiled,Peer-reviewed articleRead source →31Assessment of In Vitro Bioaccessibility and In Vivo Oral Bioavailability as Complementary Tools to Better Understand the Effect of Cooking on Methylmercury, Arsenic, and Selenium in TunaToxics 9(2):27Read source → Atlantic cod fillets lost no measurable mercury when boiled, pan-fried or oven-baked, but the concentration per 100 g rose, for example from 33 to 43 µg/kg after pan-frying.30Iodine and Mercury Content in Raw, Boiled,Peer-reviewed articleRead source → In a feeding trial with pigs, oven-cooked tuna delivered the same methylmercury to the blood as raw tuna, although laboratory digestion tests had suggested less was available.31Assessment of In Vitro Bioaccessibility and In Vivo Oral Bioavailability as Complementary Tools to Better Understand the Effect of Cooking on Methylmercury, Arsenic, and Selenium in TunaToxics 9(2):27Read source →
Canning, drying and smoking change the measured concentration mainly through water content and the species that are canned.3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →32Heavy metal content and molecular species identification in canned tuna: Insights into human food safetyMolecular Medicine ReportsRead source →33Methylmercury in fish and seafood – health risk assessment of new data from the BfR MEAL studyBfR Opinion 023/2024Read source → US canned light tuna in water had a median of 220 µg/kg total mercury, Italian cans of skipjack and yellowfin ranged from 50 to 290 µg/kg, and smoked dogfish belly flaps in Germany had 580 µg/kg methylmercury against 30–70 µg/kg in herring products.3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →32Heavy metal content and molecular species identification in canned tuna: Insights into human food safetyMolecular Medicine ReportsRead source →33Methylmercury in fish and seafood – health risk assessment of new data from the BfR MEAL studyBfR Opinion 023/2024Read source → Experimental soaking of canned or fresh tuna in a cysteine solution extracted about 13–38% of the mercury, but this is a laboratory treatment, not an approved or household method.34New Insight into Mercury Removal from Fish Meat Using aPeer-reviewed articleRead source →
Packaging and cooking materials can add metals that are not from the fish. Fish baked in aluminium foil with a lemon and salt marinade picked up 4,560–21,000 µg/kg aluminium, against under 1,140 µg/kg without the marinade and none detected when baked in glass.35Aluminum contamination of food during culinary preparation: Case study with aluminum foil and consumers’ preferencesFood Science & NutritionRead source → Resin-coated cans kept tin low in canned tuna (700 µg/kg), far below the EU limit of 200,000 µg/kg for canned food.36Determination of Tin in Canned Foods by Inductively Coupled Plasma-Mass SpectrometryPolish Journal of Environmental StudiesRead source →11Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006Official Journal of the European UnionRead source →
Does cooking reduce mercury in fish?
No: boiling, frying and baking cod left the mercury in the fillet unchanged, and concentrations rose as water was lost.30Iodine and Mercury Content in Raw, Boiled,Peer-reviewed articleRead source → Cooked tuna fed to pigs delivered the same methylmercury to the blood as raw tuna.31Assessment of In Vitro Bioaccessibility and In Vivo Oral Bioavailability as Complementary Tools to Better Understand the Effect of Cooking on Methylmercury, Arsenic, and Selenium in TunaToxics 9(2):27Read source →
Mitigation from catch to plate
The controls with measured effects act on mercury through what is caught and sold: species, size and, for some species, farming.5Assessing mercury exposure to water and fish of the Mackenzie watershed using a Bayesian network analysisIntegrated Environmental Assessment and ManagementRead source →6PCBs and Heavy Metals in Farmed, Escaped and WildPeer-reviewed articleRead source →10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source → Choosing smaller fish within a species more than halved mean mercury in northern pike and cut it more than sixfold in yellowtail, and lot testing with total mercury as a screen is built into the Codex sampling plan.5Assessing mercury exposure to water and fish of the Mackenzie watershed using a Bayesian network analysisIntegrated Environmental Assessment and ManagementRead source →9Report of the 17th Session of the Codex Committee on Contaminants in Foods (REP24/CF17)Joint FAO/WHO Food Standards Programme, Codex Alimentarius CommissionRead source →10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source → Household preparation and cooking do not lower mercury, and the measured processing reductions come from laboratory treatments not used in commercial fish.30Iodine and Mercury Content in Raw, Boiled,Peer-reviewed articleRead source →31Assessment of In Vitro Bioaccessibility and In Vivo Oral Bioavailability as Complementary Tools to Better Understand the Effect of Cooking on Methylmercury, Arsenic, and Selenium in TunaToxics 9(2):27Read source →34New Insight into Mercury Removal from Fish Meat Using aPeer-reviewed articleRead source →
For cadmium, lead and inorganic arsenic, the evidence on controls is mostly observational: higher values cluster at polluted sites, so siting of farms and fishing grounds is the main lever.7Heavy Metal Levels and Cancer Risk Assessments of the Commercial Denis, Sparus aurata Collected from Bardawil Lake and Private Fish Farm Waters as a Cultured Source, EgyptNot reportedRead source →12Scientific Opinion of the Panel on Contaminants in the Food Chain on a request from the European Commission on cadmium in foodThe EFSA JournalRead source → Feed additives tested in dosed laboratory fish lowered muscle cadmium or mercury, but the doses were far above environmental levels, so they show a mechanism, not a proven farm control.37Saccharomyces cerevisiae supplemented diets mitigate the effects of waterborne cadmium toxicity on gilthead seabream (Sparus aurata L.): growth performance, haemato-biochemical, stress biomarkers, and histopathological investigationsNot reportedRead source →38Toxicity Evaluation, Oxidative, and Immune Responses of Mercury on Nile Tilapia: Modulatory Role of Dietary Nannochloropsis oculataNot reportedRead source →
Filter findings
12 control comparisons
About this table
| Control | Material | Effects | Evidence | |||||||||||||||||||||||||||||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Select smaller fish within a speciescapture and landing · As reported | Fish | Hg_unspecified · Decreased | 1Jermilova et al. 2025 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Mercury (speciation not reported)DecreasedLower in smaller fish (observational)Mean muscle mercuryLarge versus small pike, GSL OutletFish muscle, wet weightHigh · HMI calculates the relative change from the retained source means: (300 − 740) / 740 × 100 = -59.5%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Large (≥600 mm) versus small (<600 mm) pike, same lake area. How magnitude is classified HMI editorial magnitude bands: Low is a change greater than 0% and below 25%; Moderate is 25% to below 50%; High is 50% or more, relative to that control’s own comparator. Direction is shown separately. These are descriptive display bands, not validated efficacy cutoffs, occurrence-baseline positions, statistical significance, evidence certainty, safety or net benefit. A range spanning bands retains both labels; a qualitative label has no implied percentage. Control in context Modelled mean mercury in pike under 600 mm was about two to three times lower than in pike of 600 mm or longer.
Design, applicability and operating conditions Observational comparison. Freshwater predatory fish; one basin. One study family. As reported by the source Reduces the metal in fish as caught, sold or eaten, or detects it before release. Source measurements and linked outcomes
Model-based means from monitoring data; mercury form not stated. No percentage calculated unless shown in outcomes. Wet weight unless stated. Trade-offs and implementation Not assessed unless stated. Not assessed. Not assessed. Not quantified. Not assessed. Applicability and verification Freshwater predatory fish; one basin. Lot testing. See source. Extraction limits and next actions
Provenance and assessment As disclosed by the source. Source facts and HMI calculations are distinguished above. These selected source findings do not constitute a systematic review; outcome-level appraisal remains incomplete. | |||||||||||||||||||||||||||||||||||||||||||||
| Farmed rather than wild Atlantic salmon for lower mercuryaquaculture · As reported | Fish | tHg · Decreased As_unspecified · Decreased | 1Lerøy salmon study 2020 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Total mercuryDecreasedLower in farmed salmon (observational)Mean fillet total mercuryWild versus farmedFish muscle, wet weightHigh · HMI calculates the relative change from the retained source means: (18.1 − 56.3) / 56.3 × 100 = -67.9%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Arsenic (speciation not reported)DecreasedLower in farmed salmon (observational)Mean fillet arsenicWild versus farmedFish muscle, wet weightHigh · HMI calculates the relative change from the retained source means: (860 − 2560) / 2560 × 100 = -66.4%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Farmed versus wild salmon from the same coast, 2017–2018. How magnitude is classified HMI editorial magnitude bands: Low is a change greater than 0% and below 25%; Moderate is 25% to below 50%; High is 50% or more, relative to that control’s own comparator. Direction is shown separately. These are descriptive display bands, not validated efficacy cutoffs, occurrence-baseline positions, statistical significance, evidence certainty, safety or net benefit. A range spanning bands retains both labels; a qualitative label has no implied percentage. Control in context Farmed salmon averaged 18 µg/kg total mercury against 56 µg/kg in wild salmon, while arsenic was 860 against 2,560 µg/kg.
Design, applicability and operating conditions Observational comparison. One farm and one wild stock. One study family. As reported by the source Reduces the metal in fish as caught, sold or eaten, or detects it before release. Source measurements and linked outcomes
Observational; farm feed and site not varied. No percentage calculated unless shown in outcomes. Wet weight unless stated. Trade-offs and implementation Not assessed unless stated. Not assessed. Not assessed. Not quantified. Not assessed. Applicability and verification One farm and one wild stock. Lot testing. See source. Extraction limits and next actions
Provenance and assessment As disclosed by the source. Source facts and HMI calculations are distinguished above. These selected source findings do not constitute a systematic review; outcome-level appraisal remains incomplete. | |||||||||||||||||||||||||||||||||||||||||||||
| Ranched bluefin tuna versus wild-caught adultsaquaculture · As reported | Fish | tHg · Decreased | 1Bluefin farming study 2019 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Total mercuryDecreasedLower in farmed bluefin (observational)Mean muscle total mercuryWild versus farmedFish muscle, wet weightHigh · HMI calculates the relative change from the retained source means: (610 − 1680) / 1680 × 100 = -63.7%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Farmed (Malta, 2015) versus wild (Sardinia, 2017). How magnitude is classified HMI editorial magnitude bands: Low is a change greater than 0% and below 25%; Moderate is 25% to below 50%; High is 50% or more, relative to that control’s own comparator. Direction is shown separately. These are descriptive display bands, not validated efficacy cutoffs, occurrence-baseline positions, statistical significance, evidence certainty, safety or net benefit. A range spanning bands retains both labels; a qualitative label has no implied percentage. Control in context Bluefin fattened on a Maltese farm averaged 610 µg/kg total mercury against 1,680 µg/kg in large wild bluefin from Sardinia.
Design, applicability and operating conditions Observational comparison. Ranched fish differ in size and diet from the wild fish sampled. One study family. As reported by the source Reduces the metal in fish as caught, sold or eaten, or detects it before release. Source measurements and linked outcomes
Different years and sizes; not a controlled comparison. No percentage calculated unless shown in outcomes. Wet weight unless stated. Trade-offs and implementation Not assessed unless stated. Not assessed. Not assessed. Not quantified. Not assessed. Applicability and verification Ranched fish differ in size and diet from the wild fish sampled. Lot testing. See source. Extraction limits and next actions
Provenance and assessment As disclosed by the source. Source facts and HMI calculations are distinguished above. These selected source findings do not constitute a systematic review; outcome-level appraisal remains incomplete. | |||||||||||||||||||||||||||||||||||||||||||||
| Microalga feed supplement in mercury-exposed tilapiaaquaculture · As reported | Fish | Hg_unspecified · Decreased | 1Zahran et al. 2023 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Mercury (speciation not reported)DecreasedLower with supplement in dosed fishMuscle mercurySupplemented versus basal dietFish muscle, wet weightNot quantified · No supported numerical treatment contrast is retained for this finding. A direction, market association, source-selection strategy or guidance statement alone does not establish a percentage change. Dosed fish with versus without supplement. How magnitude is classified HMI editorial magnitude bands: Low is a change greater than 0% and below 25%; Moderate is 25% to below 50%; High is 50% or more, relative to that control’s own comparator. Direction is shown separately. These are descriptive display bands, not validated efficacy cutoffs, occurrence-baseline positions, statistical significance, evidence certainty, safety or net benefit. A range spanning bands retains both labels; a qualitative label has no implied percentage. Control in context Feeding 5–10% Nannochloropsis lowered muscle mercury in tilapia dosed with mercury in water, compared with dosed fish on the basal diet.
Design, applicability and operating conditions Measured comparison. Laboratory dosing far above environmental levels. One study family. As reported by the source Reduces the metal in fish as caught, sold or eaten, or detects it before release. Source measurements and linked outcomes
Mechanistic; not a farm trial; text gives inconsistent values. No percentage calculated unless shown in outcomes. Wet weight unless stated. Trade-offs and implementation Not assessed unless stated. Not assessed. Not assessed. Not quantified. Not assessed. Applicability and verification Laboratory dosing far above environmental levels. Lot testing. See source. Extraction limits and next actions
Provenance and assessment As disclosed by the source. Source facts and HMI calculations are distinguished above. These selected source findings do not constitute a systematic review; outcome-level appraisal remains incomplete. | |||||||||||||||||||||||||||||||||||||||||||||
| Dietary yeast in cadmium-exposed seabreamaquaculture · As reported | Fish | Cd · Decreased | 1Abdel-Tawwab et al. 2023 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators CadmiumDecreasedLower with supplement in dosed fishMuscle cadmiumSupplemented versus control dietFish muscle, wet weightNot quantified · No supported numerical treatment contrast is retained for this finding. A direction, market association, source-selection strategy or guidance statement alone does not establish a percentage change. Yeast-supplemented versus unsupplemented exposed fish. How magnitude is classified HMI editorial magnitude bands: Low is a change greater than 0% and below 25%; Moderate is 25% to below 50%; High is 50% or more, relative to that control’s own comparator. Direction is shown separately. These are descriptive display bands, not validated efficacy cutoffs, occurrence-baseline positions, statistical significance, evidence certainty, safety or net benefit. A range spanning bands retains both labels; a qualitative label has no implied percentage. Control in context Dietary baker’s yeast lowered muscle cadmium in seabream exposed to 1–2 mg/L cadmium in water.
Design, applicability and operating conditions Measured comparison. Laboratory dosing far above environmental levels. One study family. As reported by the source Reduces the metal in fish as caught, sold or eaten, or detects it before release. Source measurements and linked outcomes
Printed units implausible; values not converted. No percentage calculated unless shown in outcomes. Wet weight unless stated. Trade-offs and implementation Not assessed unless stated. Not assessed. Not assessed. Not quantified. Not assessed. Applicability and verification Laboratory dosing far above environmental levels. Lot testing. See source. Extraction limits and next actions
Provenance and assessment As disclosed by the source. Source facts and HMI calculations are distinguished above. These selected source findings do not constitute a systematic review; outcome-level appraisal remains incomplete. | |||||||||||||||||||||||||||||||||||||||||||||
| Prefer younger fish of the same speciessourcing and procurement · As reported | Fish | tHg · Decreased | 1Watanabe et al. 2017 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Total mercuryDecreasedLower in young fish (observational)Mean total mercuryAdult versus young yellowtailFish muscle, wet weightHigh · HMI calculates the relative change from the retained source means: (80 − 520) / 520 × 100 = -84.6%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Young versus adult yellowtail at retail, 2014–2015. How magnitude is classified HMI editorial magnitude bands: Low is a change greater than 0% and below 25%; Moderate is 25% to below 50%; High is 50% or more, relative to that control’s own comparator. Direction is shown separately. These are descriptive display bands, not validated efficacy cutoffs, occurrence-baseline positions, statistical significance, evidence certainty, safety or net benefit. A range spanning bands retains both labels; a qualitative label has no implied percentage. Control in context Young yellowtail (inada) averaged 80 µg/kg total mercury against 520 µg/kg in natural adult yellowtail.
Design, applicability and operating conditions Observational comparison. One species and market. One study family. As reported by the source Reduces the metal in fish as caught, sold or eaten, or detects it before release. Source measurements and linked outcomes
Retail sampling; sizes not standardised. No percentage calculated unless shown in outcomes. Wet weight unless stated. Trade-offs and implementation Not assessed unless stated. Not assessed. Not assessed. Not quantified. Not assessed. Applicability and verification One species and market. Lot testing. See source. Extraction limits and next actions
Provenance and assessment As disclosed by the source. Source facts and HMI calculations are distinguished above. These selected source findings do not constitute a systematic review; outcome-level appraisal remains incomplete. | |||||||||||||||||||||||||||||||||||||||||||||
| Cysteine soaking of tuna meatfood processing · As reported | Fish | tHg · Decreased | 1Mercury removal study 2024 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Total mercuryDecreasedAbout 13–38% extracted (laboratory)Mercury removed from tuna meatTreated versus untreatedFish muscle, wet weightNot quantified · No supported numerical treatment contrast is retained for this finding. A direction, market association, source-selection strategy or guidance statement alone does not establish a percentage change. Untreated control tuna. How magnitude is classified HMI editorial magnitude bands: Low is a change greater than 0% and below 25%; Moderate is 25% to below 50%; High is 50% or more, relative to that control’s own comparator. Direction is shown separately. These are descriptive display bands, not validated efficacy cutoffs, occurrence-baseline positions, statistical significance, evidence certainty, safety or net benefit. A range spanning bands retains both labels; a qualitative label has no implied percentage. Control in context Soaking in 1.2% cysteine solution extracted about 13% of mercury from whole canned tuna and 36–38% from minced canned tuna.
Design, applicability and operating conditions Measured comparison. Laboratory treatment; not an approved process. One study family. As reported by the source Reduces the metal in fish as caught, sold or eaten, or detects it before release. Source measurements and linked outcomes
Values read from figures. No percentage calculated unless shown in outcomes. Wet weight unless stated. Trade-offs and implementation Not assessed unless stated. Not assessed. Not assessed. Not quantified. Not assessed. Applicability and verification Laboratory treatment; not an approved process. Lot testing. See source. Extraction limits and next actions
Provenance and assessment As disclosed by the source. Source facts and HMI calculations are distinguished above. These selected source findings do not constitute a systematic review; outcome-level appraisal remains incomplete. | |||||||||||||||||||||||||||||||||||||||||||||
| Use resin-coated cans for fishpackaging and storage · As reported | Fish | Sn · Decreased | 1Trandafir et al. 2012 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Total tinDecreasedLow tin in coated cansTin in canned tunaCoated tuna canFish muscle, wet weightNot quantified · No supported numerical treatment contrast is retained for this finding. A direction, market association, source-selection strategy or guidance statement alone does not establish a percentage change. Coated tuna cans versus acidic fruit and vegetable cans. How magnitude is classified HMI editorial magnitude bands: Low is a change greater than 0% and below 25%; Moderate is 25% to below 50%; High is 50% or more, relative to that control’s own comparator. Direction is shown separately. These are descriptive display bands, not validated efficacy cutoffs, occurrence-baseline positions, statistical significance, evidence certainty, safety or net benefit. A range spanning bands retains both labels; a qualitative label has no implied percentage. Control in context Tuna in resin-coated cans had 700 µg/kg tin against up to 73,680 µg/kg in acidic tomato products in uncoated cans.
Design, applicability and operating conditions Observational comparison. Canned fish. One study family. As reported by the source Reduces the metal in fish as caught, sold or eaten, or detects it before release. Source measurements and linked outcomes
Different foods compared; not a controlled can trial. No percentage calculated unless shown in outcomes. Wet weight unless stated. Trade-offs and implementation Not assessed unless stated. Not assessed. Not assessed. Not quantified. Not assessed. Applicability and verification Canned fish. Lot testing. See source. Extraction limits and next actions
Provenance and assessment As disclosed by the source. Source facts and HMI calculations are distinguished above. These selected source findings do not constitute a systematic review; outcome-level appraisal remains incomplete. | |||||||||||||||||||||||||||||||||||||||||||||
| Lot sampling for methylmercury with total mercury screeninglot acceptance and release · As reported | Fish | MeHg · Context | GuidanceCodex CCCF17 2024 HMI source record · Original source Official guidance; not an independent experimental dataset. Reused across actions without adding studies. Effects and comparators MethylmercuryDetection, not removalLot compliance decisionSampling planFish muscle, wet weightContext · No supported numerical treatment contrast is retained for this finding. A direction, market association, source-selection strategy or guidance statement alone does not establish a percentage change. Codex methylmercury limits (tuna 1,200 µg/kg; shark 1,600 µg/kg). How magnitude is classified HMI editorial magnitude bands: Low is a change greater than 0% and below 25%; Moderate is 25% to below 50%; High is 50% or more, relative to that control’s own comparator. Direction is shown separately. These are descriptive display bands, not validated efficacy cutoffs, occurrence-baseline positions, statistical significance, evidence certainty, safety or net benefit. A range spanning bands retains both labels; a qualitative label has no implied percentage. Control in context Lots are grouped by one species and comparable size; a total mercury result at or below the methylmercury limit is compliant, otherwise methylmercury is measured.
Design, applicability and operating conditions Official guidance. International trade lots. One study family. As reported by the source Reduces the metal in fish as caught, sold or eaten, or detects it before release. Source measurements and linked outcomes
Guidance; no measured effect. No percentage calculated unless shown in outcomes. Wet weight unless stated. Trade-offs and implementation Not assessed unless stated. Not assessed. Not assessed. Not quantified. Not assessed. Applicability and verification International trade lots. Lot testing. See source. Extraction limits and next actions
Provenance and assessment As disclosed by the source. Source facts and HMI calculations are distinguished above. These selected source findings do not constitute a systematic review; outcome-level appraisal remains incomplete. | |||||||||||||||||||||||||||||||||||||||||||||
| Do not rely on cooking to lower mercuryhome preparation · As reported | Fish | tHg · Increased tHg · Increased | 1Cod cooking study 2020 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Total mercuryIncreasedHigher concentration after fryingTotal mercury per kgRaw versus pan-friedFish muscle, wet weightModerate · HMI calculates the relative change from the retained source means: (43 − 33) / 33 × 100 = 30.3%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Total mercuryIncreasedHigher concentration after boilingTotal mercury per kgRaw versus boiledFish muscle, wet weightLow · HMI calculates the relative change from the retained source means: (32 − 29) / 29 × 100 = 10.3%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Raw half versus cooked half of the same fillet. How magnitude is classified HMI editorial magnitude bands: Low is a change greater than 0% and below 25%; Moderate is 25% to below 50%; High is 50% or more, relative to that control’s own comparator. Direction is shown separately. These are descriptive display bands, not validated efficacy cutoffs, occurrence-baseline positions, statistical significance, evidence certainty, safety or net benefit. A range spanning bands retains both labels; a qualitative label has no implied percentage. Control in context Boiling, pan-frying and oven-baking left mercury per fillet unchanged; concentration rose with water loss (33 to 43 µg/kg after frying).
Design, applicability and operating conditions Measured comparison. Household cooking of white fish. One study family. As reported by the source Reduces the metal in fish as caught, sold or eaten, or detects it before release. Source measurements and linked outcomes
Ten fillets per method. No percentage calculated unless shown in outcomes. Wet weight unless stated. Trade-offs and implementation Not assessed unless stated. Not assessed. Not assessed. Not quantified. Not assessed. Applicability and verification Household cooking of white fish. Lot testing. See source. Extraction limits and next actions
Provenance and assessment As disclosed by the source. Source facts and HMI calculations are distinguished above. These selected source findings do not constitute a systematic review; outcome-level appraisal remains incomplete. | |||||||||||||||||||||||||||||||||||||||||||||
| Avoid acidic marinades on fish baked in aluminium foilhome preparation · As reported | Fish | Al · Increased | 1Dordević et al. 2019 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators AluminiumIncreasedHigher with marinade in foilAluminium in baked fishUnmarinated versus marinated salmon, foilFish muscle, wet weightHigh · HMI calculates the relative change from the retained source means: (21000 − 540) / 540 × 100 = 3788.9%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Marinated versus unmarinated, foil versus glass. How magnitude is classified HMI editorial magnitude bands: Low is a change greater than 0% and below 25%; Moderate is 25% to below 50%; High is 50% or more, relative to that control’s own comparator. Direction is shown separately. These are descriptive display bands, not validated efficacy cutoffs, occurrence-baseline positions, statistical significance, evidence certainty, safety or net benefit. A range spanning bands retains both labels; a qualitative label has no implied percentage. Control in context Marinated fish baked in aluminium foil took up 4,560–21,000 µg/kg aluminium; unmarinated fish under 1,140 µg/kg and fish baked in glass none detected.
Design, applicability and operating conditions Measured comparison. Baking in foil with lemon and salt. One study family. As reported by the source Reduces the metal in fish as caught, sold or eaten, or detects it before release. Source measurements and linked outcomes
One laboratory; foil brands varied. No percentage calculated unless shown in outcomes. Wet weight unless stated. Trade-offs and implementation Not assessed unless stated. Not assessed. Not assessed. Not quantified. Not assessed. Applicability and verification Baking in foil with lemon and salt. Lot testing. See source. Extraction limits and next actions
Provenance and assessment As disclosed by the source. Source facts and HMI calculations are distinguished above. These selected source findings do not constitute a systematic review; outcome-level appraisal remains incomplete. | |||||||||||||||||||||||||||||||||||||||||||||
| Choose lower-mercury speciesdietary exposure · As reported | Fish | MeHg · Context | GuidanceFDA/EPA fish advice HMI source record · Original source Official guidance; not an independent experimental dataset. Reused across actions without adding studies. Effects and comparators MethylmercuryLower intake by species choice (guidance)Dietary methylmercuryCategory choiceFish muscle, wet weightContext · No supported numerical treatment contrast is retained for this finding. A direction, market association, source-selection strategy or guidance statement alone does not establish a percentage change. Best Choices versus Choices to Avoid categories. How magnitude is classified HMI editorial magnitude bands: Low is a change greater than 0% and below 25%; Moderate is 25% to below 50%; High is 50% or more, relative to that control’s own comparator. Direction is shown separately. These are descriptive display bands, not validated efficacy cutoffs, occurrence-baseline positions, statistical significance, evidence certainty, safety or net benefit. A range spanning bands retains both labels; a qualitative label has no implied percentage. Control in context Two to three servings a week from Best Choices such as salmon, sardines, cod and tilapia; avoid shark, swordfish, king mackerel, marlin, orange roughy, Gulf tilefish and bigeye tuna.
Design, applicability and operating conditions Official guidance. US consumers, pregnancy and childhood. One study family. As reported by the source Reduces the metal in fish as caught, sold or eaten, or detects it before release. Source measurements and linked outcomes
Guidance; categories based on FDA monitoring. No percentage calculated unless shown in outcomes. Wet weight unless stated. Trade-offs and implementation Not assessed unless stated. Not assessed. Not assessed. Not quantified. Not assessed. Applicability and verification US consumers, pregnancy and childhood. Lot testing. See source. Extraction limits and next actions
Provenance and assessment As disclosed by the source. Source facts and HMI calculations are distinguished above. These selected source findings do not constitute a systematic review; outcome-level appraisal remains incomplete. | |||||||||||||||||||||||||||||||||||||||||||||
No matching controls in this selected evidence. This is a coverage boundary, not proof that no control exists. Change or reset the filters.
Trade-offs and limits of controls
The lowest-mercury choice is not always lowest in every metal. Sardine, anchovy and mackerel, all low in mercury, sit in the EU’s higher cadmium limit groups of 100–250 µg/kg, and farming lowered both mercury and arsenic in Norwegian salmon but came with more total arsenic in a US farmed coho sample.6PCBs and Heavy Metals in Farmed, Escaped and WildPeer-reviewed articleRead source →28Determination of total arsenic and hydrophilic arsenic species in seafoodJournal of Food Composition and AnalysisRead source →11Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006Official Journal of the European UnionRead source → Flatfish, which are low in mercury, carry some of the highest total arsenic, mostly as organic arsenic, and the EU sets a higher inorganic arsenic limit of 500 µg/kg for flatfish, haddock and anglerfish.16Commission Regulation (EU) 2025/1891 of 17 September 2025 amending Regulation (EU) 2023/915 as regards maximum levels of inorganic arsenic in fish and other seafoodOfficial Journal of the European UnionRead source →39Arsenic levels in fish and shellfish from the North SeaJournal of Experimental Marine Biology and EcologyRead source →
Avoiding fish to avoid mercury also removes a main dietary source of omega-3 fatty acids.8Advice About Eating Fish — For Those Who Might Become or Are Pregnant or Breastfeeding and Children Ages 1 to 11 YearsU.S. FDA and U.S. EPARead source →40Statement on the benefits of fish/seafood consumption compared to the risks of methylmercury in fish/seafoodEFSA Journal 2015;13(1):3982, 36 pp.Read source → EFSA’s scientific committee and US federal advice both pair limits on high-mercury species with encouragement to eat lower-mercury fish, rather than advising against fish in general.8Advice About Eating Fish — For Those Who Might Become or Are Pregnant or Breastfeeding and Children Ages 1 to 11 YearsU.S. FDA and U.S. EPARead source →40Statement on the benefits of fish/seafood consumption compared to the risks of methylmercury in fish/seafoodEFSA Journal 2015;13(1):3982, 36 pp.Read source →
Testing fish for metals
A useful fish test reports the analyte species that the limit uses, on wet weight, with a quantification limit well below that limit.9Report of the 17th Session of the Codex Committee on Contaminants in Foods (REP24/CF17)Joint FAO/WHO Food Standards Programme, Codex Alimentarius CommissionRead source →11Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006Official Journal of the European UnionRead source →41Australia New Zealand Food Standards Code - Schedule 19 - Maximum levels of contaminants and natural toxicantsFederal Register of Legislation, Authorised Version F2024C00908Read source → The EU and Codex mercury limits for most fish (500 µg/kg) and the EU inorganic arsenic limit (100 µg/kg) need methods that can see far lower, as FDA’s 4 µg/kg lead reporting limit and EFSA’s speciated arsenic data show is achievable.3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →4Dietary exposure to inorganic arsenic in the European populationEFSA Journal 2014;12(3):3597Read source →11Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006Official Journal of the European UnionRead source →16Commission Regulation (EU) 2025/1891 of 17 September 2025 amending Regulation (EU) 2023/915 as regards maximum levels of inorganic arsenic in fish and other seafoodOfficial Journal of the European UnionRead source →
Codex allows total mercury as a screen: a sample at or below the methylmercury limit for total mercury is compliant, and only higher samples need methylmercury analysis.9Report of the 17th Session of the Codex Committee on Contaminants in Foods (REP24/CF17)Joint FAO/WHO Food Standards Programme, Codex Alimentarius CommissionRead source →10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source → Its sampling plan groups lots by one species and comparable size and takes muscle near the tail for tuna, because mercury varies with fish size and body part.9Report of the 17th Session of the Codex Committee on Contaminants in Foods (REP24/CF17)Joint FAO/WHO Food Standards Programme, Codex Alimentarius CommissionRead source →
Many surveys in the evidence report dry-weight results, mercury without stating its form, or total arsenic only, and some measured mercury after dry ashing at 450–500 °C, a step that can lose mercury.42Survey of lead, cadmium, mercury and arsenic in seafood purchased in Campania, ItalyFood Additives & Contaminants: Part B: SurveillanceRead source →43Detection of heavy metals bio-accumulation in scombrids for the determination of possible health hazardAfrican Journal of Food Science and Technology 6(4):098-107Read source → These results stay on the page but cannot be compared with wet-weight limits or with speciated results, and several are held because their values conflict with their own methods.13Hazardous effects of heavy metal pollution on Nile tilapia in the aquatic ecosystem of the Eastern Delta in EgyptBMC Veterinary ResearchRead source →14Health Risk Assessment of Heavy Metals in Marine Fish Caught from the Northwest Persian GulfBiological Trace Element ResearchRead source →42Survey of lead, cadmium, mercury and arsenic in seafood purchased in Campania, ItalyFood Additives & Contaminants: Part B: SurveillanceRead source →43Detection of heavy metals bio-accumulation in scombrids for the determination of possible health hazardAfrican Journal of Food Science and Technology 6(4):098-107Read source →
Why do some studies report very high lead or cadmium in fish?
Several of the highest values cannot be reconciled with their own papers: one Egyptian tilapia study prints mg/kg where its methods state µg/kg, a Persian Gulf study prints species means outside their own ranges, and an Indian survey’s intake figures imply values a thousand times higher than its table.13Hazardous effects of heavy metal pollution on Nile tilapia in the aquatic ecosystem of the Eastern Delta in EgyptBMC Veterinary ResearchRead source →14Health Risk Assessment of Heavy Metals in Marine Fish Caught from the Northwest Persian GulfBiological Trace Element ResearchRead source →15ICP-MS-based quantitative analysis and risk assessment of metal(loid)s in fish species from Chennai, IndiaFrontiers in Public HealthRead source → These results are shown but held from comparisons.
Buying and verifying fish
Ask suppliers for the species and, where possible, the size or weight class and the catch or farm area, because mercury depends most on these.5Assessing mercury exposure to water and fish of the Mackenzie watershed using a Bayesian network analysisIntegrated Environmental Assessment and ManagementRead source →9Report of the 17th Session of the Codex Committee on Contaminants in Foods (REP24/CF17)Joint FAO/WHO Food Standards Programme, Codex Alimentarius CommissionRead source →10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source → Lot results should be on wet weight, name the analyte as total mercury or methylmercury, and be compared with the limit for that species in the destination market.9Report of the 17th Session of the Codex Committee on Contaminants in Foods (REP24/CF17)Joint FAO/WHO Food Standards Programme, Codex Alimentarius CommissionRead source →11Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006Official Journal of the European UnionRead source →41Australia New Zealand Food Standards Code - Schedule 19 - Maximum levels of contaminants and natural toxicantsFederal Register of Legislation, Authorised Version F2024C00908Read source →
Limits differ by market and by species group. The EU sets total mercury at 300 µg/kg for anchovy, sardine, herring, mackerel, cod, Alaska pollock, salmon and trout, 500 µg/kg for most other fish and 1,000 µg/kg for large predators such as tuna, swordfish, shark and pike, with cadmium at 50–250 µg/kg and lead at 300 µg/kg.11Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006Official Journal of the European UnionRead source → Australia and New Zealand use mean mercury levels of 500 or 1,000 µg/kg depending on species, and China sets methylmercury at 500 µg/kg for non-carnivorous fish, 1,000 µg/kg for carnivorous fish and 1,200 µg/kg for tuna.44China Releases the Standard for Maximum Levels of Contaminants in Foods (USDA FAS GAIN Report CH2023-0040, unofficial translation of GB 2762-2022)USDA Foreign Agricultural Service, Global Agricultural Information Network (GAIN), Report Number CH2023-0040Read source →41Australia New Zealand Food Standards Code - Schedule 19 - Maximum levels of contaminants and natural toxicantsFederal Register of Legislation, Authorised Version F2024C00908Read source → For inorganic arsenic, the EU has applied 100 µg/kg to most fish and 500 µg/kg to flatfish, haddock and anglerfish since 8 October 2025, while Australia and New Zealand set 2,000 µg/kg.16Commission Regulation (EU) 2025/1891 of 17 September 2025 amending Regulation (EU) 2023/915 as regards maximum levels of inorganic arsenic in fish and other seafoodOfficial Journal of the European UnionRead source →41Australia New Zealand Food Standards Code - Schedule 19 - Maximum levels of contaminants and natural toxicantsFederal Register of Legislation, Authorised Version F2024C00908Read source →
Canned fish carry two extra checks: tin from the can, limited to 200 mg/kg in the EU and 250 mg/kg under Codex and FSANZ, and the species inside, since tuna cans labelled light, skipjack or yellowfin differ in mercury.36Determination of Tin in Canned Foods by Inductively Coupled Plasma-Mass SpectrometryPolish Journal of Environmental StudiesRead source →32Heavy metal content and molecular species identification in canned tuna: Insights into human food safetyMolecular Medicine ReportsRead source →11Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006Official Journal of the European UnionRead source →41Australia New Zealand Food Standards Code - Schedule 19 - Maximum levels of contaminants and natural toxicantsFederal Register of Legislation, Authorised Version F2024C00908Read source →
Exposure from fish
Fish is the main dietary source of methylmercury, and how much it adds depends on the species, portion and how often it is eaten.23Evaluation of Certain Food Additives and Contaminants (Methylmercury), 61st Meeting of JECFAWHO Technical Report Series 922Read source →40Statement on the benefits of fish/seafood consumption compared to the risks of methylmercury in fish/seafoodEFSA Journal 2015;13(1):3982, 36 pp.Read source → JECFA set a tolerable weekly intake of 1.6 µg/kg body weight for methylmercury and EFSA 1.3 µg/kg; EFSA’s scientific committee found that high consumers of predatory fish in several countries could exceed it.23Evaluation of Certain Food Additives and Contaminants (Methylmercury), 61st Meeting of JECFAWHO Technical Report Series 922Read source →40Statement on the benefits of fish/seafood consumption compared to the risks of methylmercury in fish/seafoodEFSA Journal 2015;13(1):3982, 36 pp.Read source →
US advice for pregnancy and breastfeeding recommends 8–12 ounces (two to three servings) a week from lower-mercury choices such as salmon, sardines, cod, pollock, tilapia and trout, and avoiding king mackerel, marlin, orange roughy, shark, swordfish, Gulf of Mexico tilefish and bigeye tuna.8Advice About Eating Fish — For Those Who Might Become or Are Pregnant or Breastfeeding and Children Ages 1 to 11 YearsU.S. FDA and U.S. EPARead source → These categories match the measured species differences on this page.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source →8Advice About Eating Fish — For Those Who Might Become or Are Pregnant or Breastfeeding and Children Ages 1 to 11 YearsU.S. FDA and U.S. EPARead source →27The First Hong Kong Total Diet Study: Metallic ContaminantsCentre for Food Safety, Food and Environmental Hygiene Department, Government of the Hong Kong Special Administrative RegionRead source →
No source measured metals in a fish-containing food together with the fish that went into it, so finished-product results cannot be traced back to the raw fish. Fish fingers in the US Total Diet Study had 6 µg/kg total mercury and baked fish fillets in Germany 20 µg/kg methylmercury.3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →33Methylmercury in fish and seafood – health risk assessment of new data from the BfR MEAL studyBfR Opinion 023/2024Read source →
Evidence review and remaining gaps
This assessment covers every source record in the HMI library that is tagged to fish or mentions it (1,341 records), every matching fish row in WHO GEMS/Food and the FDA Total Diet Study, and the HMI index rows that route sources to fish; each has a recorded decision based on its content.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source → About 250 sources supplied finfish occurrence results, and 273 extracted results are held because their values conflict with their own papers.13Hazardous effects of heavy metal pollution on Nile tilapia in the aquatic ecosystem of the Eastern Delta in EgyptBMC Veterinary ResearchRead source →14Health Risk Assessment of Heavy Metals in Marine Fish Caught from the Northwest Persian GulfBiological Trace Element ResearchRead source →15ICP-MS-based quantitative analysis and risk assessment of metal(loid)s in fish species from Chennai, IndiaFrontiers in Public HealthRead source → Remaining gaps are per-fish supplementary tables that were not in the library, a handful of reports with no readable primary text, and EFSA and national datasets that mix fish with shellfish.21Assessment of the dietary exposure to arsenic, cadmium, lead and mercury of the population of the EU Member StatesReports on tasks for scientific cooperation, SCOOP Task 3.2.11Read source →4525th Australian Total Diet StudyFood Standards Australia New ZealandRead source →
References identify the sources used in these answers. The Sources index preserves additional discovery links; inclusion there does not mean a source has been reviewed for this assessment. Corrections, completed searches, new direct evidence and changes in requirements should reopen the relevant answer.
Fish FAQs
What heavy metals are found in fish?
Mercury, mostly as methylmercury, is the metal found at levels that matter in fish; lead and cadmium are usually low in monitored fish muscle, and arsenic is mostly in organic forms.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source →3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →4Dietary exposure to inorganic arsenic in the European populationEFSA Journal 2014;12(3):3597Read source →26Risk assessment of small organoarsenic species in foodEFSA JournalRead source → Fish can also contain nickel, chromium, aluminium and tin, usually from processing, packaging or polluted water.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →35Aluminum contamination of food during culinary preparation: Case study with aluminum foil and consumers’ preferencesFood Science & NutritionRead source →36Determination of Tin in Canned Foods by Inductively Coupled Plasma-Mass SpectrometryPolish Journal of Environmental StudiesRead source →
How does mercury get into fish?
Methylmercury builds up through the food chain, so large, old and predatory fish carry the most.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source →23Evaluation of Certain Food Additives and Contaminants (Methylmercury), 61st Meeting of JECFAWHO Technical Report Series 922Read source → In northern pike, fish 600 mm or longer had about two to three times the mercury of smaller pike.5Assessing mercury exposure to water and fish of the Mackenzie watershed using a Bayesian network analysisIntegrated Environmental Assessment and ManagementRead source →
Which fish have the lowest mercury?
Salmon, trout, sardines, herring, anchovy, carp, tilapia, cod and pollock are consistently low; swordfish, shark, marlin, king mackerel and large tuna are highest.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source →3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →8Advice About Eating Fish — For Those Who Might Become or Are Pregnant or Breastfeeding and Children Ages 1 to 11 YearsU.S. FDA and U.S. EPARead source →27The First Hong Kong Total Diet Study: Metallic ContaminantsCentre for Food Safety, Food and Environmental Hygiene Department, Government of the Hong Kong Special Administrative RegionRead source → In EFSA’s European data, swordfish averaged about 1,212 µg/kg total mercury and salmon and trout about 33 µg/kg.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source →
Does where fish come from affect its metal levels?
For mercury, species and size matter more than country; origin comparisons for the same species are few and mostly use purchase country rather than catch area.29Determination of toxic metals in canned tuna sold in developed and developing countries: Health risk assessment associated with human consumptionMarine Pollution BulletinRead source →10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source → For lead and cadmium, origin matters most at polluted rivers, lagoons and coasts, where some local surveys report much higher values than national monitoring.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →7Heavy Metal Levels and Cancer Risk Assessments of the Commercial Denis, Sparus aurata Collected from Bardawil Lake and Private Fish Farm Waters as a Cultured Source, EgyptNot reportedRead source →
Is farmed fish safer than wild fish?
For mercury, farmed salmon, bluefin tuna and yellowtail measured lower than wild fish in the same studies.6PCBs and Heavy Metals in Farmed, Escaped and WildPeer-reviewed articleRead source →10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source →24Bluefin Tuna (Thunnus thynnus L.) MusclePeer-reviewed articleRead source → This did not hold for every metal: arsenic was higher in a farmed US coho salmon, and farmed fish in polluted water can carry more cadmium or lead.7Heavy Metal Levels and Cancer Risk Assessments of the Commercial Denis, Sparus aurata Collected from Bardawil Lake and Private Fish Farm Waters as a Cultured Source, EgyptNot reportedRead source →28Determination of total arsenic and hydrophilic arsenic species in seafoodJournal of Food Composition and AnalysisRead source →
How much mercury is in canned tuna?
US canned light tuna in water had a median of 220 µg/kg total mercury, and Italian cans of skipjack and yellowfin ranged from 50 to 290 µg/kg.3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →32Heavy metal content and molecular species identification in canned tuna: Insights into human food safetyMolecular Medicine ReportsRead source → Canned tuna bought in 36 countries had country means from 20 to 950 µg/kg, all below the Codex tuna limit of 1,200 µg/kg methylmercury.9Report of the 17th Session of the Codex Committee on Contaminants in Foods (REP24/CF17)Joint FAO/WHO Food Standards Programme, Codex Alimentarius CommissionRead source →29Determination of toxic metals in canned tuna sold in developed and developing countries: Health risk assessment associated with human consumptionMarine Pollution BulletinRead source →
What is the difference between total mercury and methylmercury in fish?
Total mercury counts all forms; methylmercury is the toxic organic form that makes up most of it in fish muscle, about 60–90% in Japanese retail fish.10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source → Limits use either one, so a result must name which was measured.9Report of the 17th Session of the Codex Committee on Contaminants in Foods (REP24/CF17)Joint FAO/WHO Food Standards Programme, Codex Alimentarius CommissionRead source →11Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006Official Journal of the European UnionRead source →44China Releases the Standard for Maximum Levels of Contaminants in Foods (USDA FAS GAIN Report CH2023-0040, unofficial translation of GB 2762-2022)USDA Foreign Agricultural Service, Global Agricultural Information Network (GAIN), Report Number CH2023-0040Read source →
Is the arsenic in fish dangerous?
Most arsenic in fish is arsenobetaine, which EFSA notes is widely assumed to be of no toxicological concern; inorganic arsenic, the form of concern, averaged 0.7–20 µg/kg across European fish species at the lower bound.4Dietary exposure to inorganic arsenic in the European populationEFSA Journal 2014;12(3):3597Read source →26Risk assessment of small organoarsenic species in foodEFSA JournalRead source → The EU now limits inorganic arsenic in fish to 100 µg/kg, or 500 µg/kg for flatfish, haddock and anglerfish.16Commission Regulation (EU) 2025/1891 of 17 September 2025 amending Regulation (EU) 2023/915 as regards maximum levels of inorganic arsenic in fish and other seafoodOfficial Journal of the European UnionRead source →
Are there legal limits for heavy metals in fish?
Yes: the EU sets total mercury at 300–1,000 µg/kg by species, cadmium at 50–250 µg/kg, lead at 300 µg/kg and inorganic arsenic at 100–500 µg/kg in fish muscle.11Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006Official Journal of the European UnionRead source →16Commission Regulation (EU) 2025/1891 of 17 September 2025 amending Regulation (EU) 2023/915 as regards maximum levels of inorganic arsenic in fish and other seafoodOfficial Journal of the European UnionRead source → Codex sets methylmercury at 1,200 µg/kg for tuna and 1,600 µg/kg for shark, and the US uses a 1 mg/kg methylmercury action level.9Report of the 17th Session of the Codex Committee on Contaminants in Foods (REP24/CF17)Joint FAO/WHO Food Standards Programme, Codex Alimentarius CommissionRead source →46Toxicological Profile for MercuryU.S. Department of Health and Human Services, Public Health Service, Agency for Toxic Substances and Disease RegistryRead source →
Does cooking fish remove mercury?
No: cooking leaves mercury in the fish and raises its concentration as water is lost, as boiled, fried and baked cod showed.30Iodine and Mercury Content in Raw, Boiled,Peer-reviewed articleRead source → Cooked tuna delivered as much methylmercury to the blood of test animals as raw tuna.31Assessment of In Vitro Bioaccessibility and In Vivo Oral Bioavailability as Complementary Tools to Better Understand the Effect of Cooking on Methylmercury, Arsenic, and Selenium in TunaToxics 9(2):27Read source →
Can processing remove heavy metals from fish?
No ordinary processing step in the evidence lowered mercury; a laboratory cysteine soak removed about 13–38% of mercury from tuna, but it is not an approved commercial or household method.34New Insight into Mercury Removal from Fish Meat Using aPeer-reviewed articleRead source → Cooking, canning and drying change concentrations mainly through water loss.3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →30Iodine and Mercury Content in Raw, Boiled,Peer-reviewed articleRead source →
Do fish oil supplements contain mercury?
Fish oil supplements tested in Serbia averaged 1.9 µg/kg mercury, with a maximum of 5.7 µg/kg.17Mercury Content in Fish Oil Food Supplements and Associated Health RiskProceedings 2023, 91, 364 (MDPI Proceedings — 14th European Nutrition Conference FENS 2023)Read source → The EU limit for mercury in food supplements is 100 µg/kg.11Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006Official Journal of the European UnionRead source →
Which fish should pregnant women and children choose?
US advice recommends 8–12 ounces (two to three servings) a week of lower-mercury fish such as salmon, sardines, cod, pollock, tilapia and trout, and avoiding shark, swordfish, king mackerel, marlin, orange roughy, Gulf tilefish and bigeye tuna.8Advice About Eating Fish — For Those Who Might Become or Are Pregnant or Breastfeeding and Children Ages 1 to 11 YearsU.S. FDA and U.S. EPARead source → This follows the measured species differences in mercury.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source →27The First Hong Kong Total Diet Study: Metallic ContaminantsCentre for Food Safety, Food and Environmental Hygiene Department, Government of the Hong Kong Special Administrative RegionRead source →
How much fish is safe to eat each week?
No single amount applies to every fish: national advice sets servings by species group and life stage, such as two to three servings a week of lower-mercury fish in US advice for pregnancy.8Advice About Eating Fish — For Those Who Might Become or Are Pregnant or Breastfeeding and Children Ages 1 to 11 YearsU.S. FDA and U.S. EPARead source →40Statement on the benefits of fish/seafood consumption compared to the risks of methylmercury in fish/seafoodEFSA Journal 2015;13(1):3982, 36 pp.Read source → JECFA’s tolerable weekly intake for methylmercury is 1.6 µg/kg body weight; how quickly a diet reaches it depends on the species eaten.23Evaluation of Certain Food Additives and Contaminants (Methylmercury), 61st Meeting of JECFAWHO Technical Report Series 922Read source →
Should I stop eating fish because of mercury?
Health agencies advise choosing lower-mercury species rather than avoiding fish, because fish supply omega-3 fatty acids and other nutrients.8Advice About Eating Fish — For Those Who Might Become or Are Pregnant or Breastfeeding and Children Ages 1 to 11 YearsU.S. FDA and U.S. EPARead source →40Statement on the benefits of fish/seafood consumption compared to the risks of methylmercury in fish/seafoodEFSA Journal 2015;13(1):3982, 36 pp.Read source → Limiting the highest-mercury species makes the largest difference to intake.40Statement on the benefits of fish/seafood consumption compared to the risks of methylmercury in fish/seafoodEFSA Journal 2015;13(1):3982, 36 pp.Read source →
Do fish fingers and other fish products contain heavy metals?
They are usually low in mercury because they are made from white fish: US fish sticks had 6 µg/kg total mercury and German baked fish fillets 20 µg/kg methylmercury.3FY2018-FY2020 TDS Elements Analytical ResultsFDA Total Diet StudyRead source →33Methylmercury in fish and seafood – health risk assessment of new data from the BfR MEAL studyBfR Opinion 023/2024Read source → No study measured a product alongside the fish used to make it.
Are smaller fish lower in mercury?
Within a species, yes in the measured studies: young yellowtail averaged 80 µg/kg against 520 µg/kg in adults, and pike under 600 mm had less than half the mercury of larger pike.5Assessing mercury exposure to water and fish of the Mackenzie watershed using a Bayesian network analysisIntegrated Environmental Assessment and ManagementRead source →10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source →
Can aluminium foil add metals to cooked fish?
Yes, with acidic or salty marinades: fish baked in foil with lemon and salt took up 4,560–21,000 µg/kg aluminium, while fish baked in glass had none detected.35Aluminum contamination of food during culinary preparation: Case study with aluminum foil and consumers’ preferencesFood Science & NutritionRead source →
Is organic or sustainably labelled fish lower in metals?
No source in the evidence compared organic-certified or eco-labelled fish with conventional fish for metals, so there is no measured answer. Species, size and the water the fish lived in are the measured drivers.1Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodEFSA Journal 2012;10(12):2985Read source →5Assessing mercury exposure to water and fish of the Mackenzie watershed using a Bayesian network analysisIntegrated Environmental Assessment and ManagementRead source →
How is fish tested for mercury?
Laboratories measure total mercury and, where needed, methylmercury by speciation methods; Codex treats a total mercury result at or below the methylmercury limit as compliant.9Report of the 17th Session of the Codex Committee on Contaminants in Foods (REP24/CF17)Joint FAO/WHO Food Standards Programme, Codex Alimentarius CommissionRead source →10Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishFood Hygiene and Safety ScienceRead source → Samples are taken from muscle, near the tail for tuna, in lots of one species and size.9Report of the 17th Session of the Codex Committee on Contaminants in Foods (REP24/CF17)Joint FAO/WHO Food Standards Programme, Codex Alimentarius CommissionRead source →
References
Works cited on this page, in citation-number order. See Sources for this page’s source inventory. Each title links to a source record with bibliographic details, reported findings, and document provenance.
- Scientific Opinion on the Risk for Public Health Related to the Presence of Mercury and Methylmercury in FoodGovernment
- GEMS/Food Contaminants database heavy-metal exportsDataset
- FY2018-FY2020 TDS Elements Analytical ResultsDataset
- Dietary exposure to inorganic arsenic in the European populationGovernment
- Assessing mercury exposure to water and fish of the Mackenzie watershed using a Bayesian network analysisPeer-reviewed
- PCBs and Heavy Metals in Farmed, Escaped and WildPeer-reviewed
- Heavy Metal Levels and Cancer Risk Assessments of the Commercial Denis, Sparus aurata Collected from Bardawil Lake and Private Fish Farm Waters as a Cultured Source, EgyptPeer-reviewed
- Advice About Eating Fish — For Those Who Might Become or Are Pregnant or Breastfeeding and Children Ages 1 to 11 YearsGovernment
- Report of the 17th Session of the Codex Committee on Contaminants in Foods (REP24/CF17)Government
- Surveillance of Total Mercury and Methylmercury Concentrations in Retail FishPeer-reviewed
- Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006Regulation
- Scientific Opinion of the Panel on Contaminants in the Food Chain on a request from the European Commission on cadmium in foodGovernment
- Hazardous effects of heavy metal pollution on Nile tilapia in the aquatic ecosystem of the Eastern Delta in EgyptPeer-reviewed
- Health Risk Assessment of Heavy Metals in Marine Fish Caught from the Northwest Persian GulfPeer-reviewed
- ICP-MS-based quantitative analysis and risk assessment of metal(loid)s in fish species from Chennai, IndiaPeer-reviewed
- Commission Regulation (EU) 2025/1891 of 17 September 2025 amending Regulation (EU) 2023/915 as regards maximum levels of inorganic arsenic in fish and other seafoodRegulation
- Mercury Content in Fish Oil Food Supplements and Associated Health RiskConference
- Mercury Exposure from the Consumption of Dietary Supplements Containing Vegetable, Cod Liver, and Shark Liver OilsPeer-reviewed
- Determination of Inorganic Arsenic in Seaweed and Seafood by LC-ICP-MS: Method ValidationPeer-reviewed
- Chemical characterization of baby food consumed in ItalyPeer-reviewed
- Assessment of the dietary exposure to arsenic, cadmium, lead and mercury of the population of the EU Member StatesGovernment
- Determination of Total Inorganic Arsenic in Fish, Shellfish and Fish ProductsPeer-reviewed
- Evaluation of Certain Food Additives and Contaminants (Methylmercury), 61st Meeting of JECFAGovernment
- Bluefin Tuna (Thunnus thynnus L.) MusclePeer-reviewed
- Scientific Opinion on Lead in FoodGovernment
- Risk assessment of small organoarsenic species in foodGovernment
- The First Hong Kong Total Diet Study: Metallic ContaminantsGovernment
- Determination of total arsenic and hydrophilic arsenic species in seafoodPeer-reviewed
- Determination of toxic metals in canned tuna sold in developed and developing countries: Health risk assessment associated with human consumptionPeer-reviewed
- Iodine and Mercury Content in Raw, Boiled,Peer-reviewed
- Assessment of In Vitro Bioaccessibility and In Vivo Oral Bioavailability as Complementary Tools to Better Understand the Effect of Cooking on Methylmercury, Arsenic, and Selenium in TunaPeer-reviewed
- Heavy metal content and molecular species identification in canned tuna: Insights into human food safetyPeer-reviewed
- Methylmercury in fish and seafood – health risk assessment of new data from the BfR MEAL studyGovernment
- New Insight into Mercury Removal from Fish Meat Using aPeer-reviewed
- Aluminum contamination of food during culinary preparation: Case study with aluminum foil and consumers’ preferencesPeer-reviewed
- Determination of Tin in Canned Foods by Inductively Coupled Plasma-Mass SpectrometryPeer-reviewed
- Saccharomyces cerevisiae supplemented diets mitigate the effects of waterborne cadmium toxicity on gilthead seabream (Sparus aurata L.): growth performance, haemato-biochemical, stress biomarkers, and histopathological investigationsPeer-reviewed
- Toxicity Evaluation, Oxidative, and Immune Responses of Mercury on Nile Tilapia: Modulatory Role of Dietary Nannochloropsis oculataPeer-reviewed
- Arsenic levels in fish and shellfish from the North SeaPeer-reviewed
- Statement on the benefits of fish/seafood consumption compared to the risks of methylmercury in fish/seafoodGovernment
- Australia New Zealand Food Standards Code - Schedule 19 - Maximum levels of contaminants and natural toxicantsRegulation
- Survey of lead, cadmium, mercury and arsenic in seafood purchased in Campania, ItalyPeer-reviewed
- Detection of heavy metals bio-accumulation in scombrids for the determination of possible health hazardPeer-reviewed
- China Releases the Standard for Maximum Levels of Contaminants in Foods (USDA FAS GAIN Report CH2023-0040, unofficial translation of GB 2762-2022)Regulation
- 25th Australian Total Diet StudyGovernment
- Toxicological Profile for MercuryGovernment
Sources
Browse Fish Sources for sources cited on this page and additional discovery candidates. The searchable index distinguishes verified citation use from discovery relationships whose relevance has not been established.
Update history
22 October 2026 — Rebuilt from every fish record in the library: WHO GEMS/Food and FDA monitoring results, about 250 survey, total diet and monitoring sources, same-species references, verified limits and stage-led controls.
