Swordfish in the HMI library has 187 reported results for lead, cadmium, total arsenic, inorganic arsenic, dimethylarsinic acid, total mercury, methylmercury, mercury, chromium, tin, Cu, Se, Se(IV), Se(VI), SeCys, SeMet and tSe from 23 sources.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Determination of Geographical and Seasonal Variations of Heavy Metals in Swordfish (Xiphias gladius) and Yellowfin Tuna (Thunnus albacares)International Journal of Current Science Research and ReviewRead source →3Assessment of metal levels in foodstuffs from the Region of Valencia (Spain)Toxicology Reports 5 (2018) 654-670Read source →4Heavy metals content in fresh tuna and swordfish caught from Hindian and Pacific Oceans: Health risk assessment of dietary exposureVeterinary WorldRead source →5Determination of toxic elements (mercury, cadmium, lead, tin and arsenic) in fish and shellfish samples. Risk assessment for the consumersEnvironment InternationalRead source →6Health Risk Assessment of Some Heavy Metals from Canned Tuna and Fish in Tijuana, MexicoHealth ScopeRead source →
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Metals measured:
Lead, cadmium, total arsenic, inorganic arsenic, dimethylarsinic acid and total mercury and others, in 187 results from 23 sources.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Determination of Geographical and Seasonal Variations of Heavy Metals in Swordfish (Xiphias gladius) and Yellowfin Tuna (Thunnus albacares)International Journal of Current Science Research and ReviewRead source →3Assessment of metal levels in foodstuffs from the Region of Valencia (Spain)Toxicology Reports 5 (2018) 654-670Read source →4Heavy metals content in fresh tuna and swordfish caught from Hindian and Pacific Oceans: Health risk assessment of dietary exposureVeterinary WorldRead source →
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Main drivers:
Form, basis and where the swordfish was sampled; reporting limits decide how many results are non-detects.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Determination of Geographical and Seasonal Variations of Heavy Metals in Swordfish (Xiphias gladius) and Yellowfin Tuna (Thunnus albacares)International Journal of Current Science Research and ReviewRead source →3Assessment of metal levels in foodstuffs from the Region of Valencia (Spain)Toxicology Reports 5 (2018) 654-670Read source →4Heavy metals content in fresh tuna and swordfish caught from Hindian and Pacific Oceans: Health risk assessment of dietary exposureVeterinary WorldRead source →
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Practical framing:
Ask for lot results with a quantification limit well below the limit that applies in the destination market.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Determination of Geographical and Seasonal Variations of Heavy Metals in Swordfish (Xiphias gladius) and Yellowfin Tuna (Thunnus albacares)International Journal of Current Science Research and ReviewRead source →3Assessment of metal levels in foodstuffs from the Region of Valencia (Spain)Toxicology Reports 5 (2018) 654-670Read source →4Heavy metals content in fresh tuna and swordfish caught from Hindian and Pacific Oceans: Health risk assessment of dietary exposureVeterinary WorldRead source →
Swordfish overview
Swordfish in the HMI library has 187 reported results for lead, cadmium, total arsenic, inorganic arsenic, dimethylarsinic acid, total mercury, methylmercury, mercury, chromium, tin, Cu, Se, Se(IV), Se(VI), SeCys, SeMet and tSe from 23 sources.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Determination of Geographical and Seasonal Variations of Heavy Metals in Swordfish (Xiphias gladius) and Yellowfin Tuna (Thunnus albacares)International Journal of Current Science Research and ReviewRead source →3Assessment of metal levels in foodstuffs from the Region of Valencia (Spain)Toxicology Reports 5 (2018) 654-670Read source →4Heavy metals content in fresh tuna and swordfish caught from Hindian and Pacific Oceans: Health risk assessment of dietary exposureVeterinary WorldRead source →5Determination of toxic elements (mercury, cadmium, lead, tin and arsenic) in fish and shellfish samples. Risk assessment for the consumersEnvironment InternationalRead source →6Health Risk Assessment of Some Heavy Metals from Canned Tuna and Fish in Tijuana, MexicoHealth ScopeRead source → WHO GEMS/Food submissions reported lead in swordfish, as sold from 839 results in 3 reporting regions, with subgroup medians below 20 µg/kg, mostly non-detects.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → For cadmium, GEMS/Food gave subgroup medians from 30 to 53 µg/kg from 1,146 results.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
Across 3 other studies of ordinary farms and markets, reported lead means and medians on an as-sold or fresh-weight basis ranged from 10.7 µg/kg (Marín et al. 2018) to 119 µg/kg (Rodriguez-Mendivil et al. 2019).3Assessment of metal levels in foodstuffs from the Region of Valencia (Spain)Toxicology Reports 5 (2018) 654-670Read source →6Health Risk Assessment of Some Heavy Metals from Canned Tuna and Fish in Tijuana, MexicoHealth ScopeRead source → For cadmium, 4 studies on an as-sold or fresh-weight basis reported means and medians from 2.2 µg/kg (Rodriguez-Mendivil et al. 2019) to 92.5 µg/kg (Marín et al. 2018).3Assessment of metal levels in foodstuffs from the Region of Valencia (Spain)Toxicology Reports 5 (2018) 654-670Read source →6Health Risk Assessment of Some Heavy Metals from Canned Tuna and Fish in Tijuana, MexicoHealth ScopeRead source →
For a buyer the practical points are the form bought, the basis a result is reported on, where the swordfish came from and the laboratory’s reporting limit. Testing finds contamination but does not remove it.
What counts as swordfish
This page covers swordfish in 2 forms kept separate in every comparison: swordfish, as sold (178 results) and swordfish, peeled or flesh (9 results).1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Determination of Geographical and Seasonal Variations of Heavy Metals in Swordfish (Xiphias gladius) and Yellowfin Tuna (Thunnus albacares)International Journal of Current Science Research and ReviewRead source →3Assessment of metal levels in foodstuffs from the Region of Valencia (Spain)Toxicology Reports 5 (2018) 654-670Read source →4Heavy metals content in fresh tuna and swordfish caught from Hindian and Pacific Oceans: Health risk assessment of dietary exposureVeterinary WorldRead source →5Determination of toxic elements (mercury, cadmium, lead, tin and arsenic) in fish and shellfish samples. Risk assessment for the consumersEnvironment InternationalRead source →6Health Risk Assessment of Some Heavy Metals from Canned Tuna and Fish in Tijuana, MexicoHealth ScopeRead source →
Results stay on the basis each source reports: as sold or fresh weight, dry weight, or unstated. Dry-weight, as-sold and unstated results are never pooled, and no moisture conversion is applied.
Heavy metal contamination profile of swordfish
The table holds every extracted swordfish result: one row for each statistic a source reports for a form, group and metal, 187 rows in all, grouped by metal and form; percentiles, ranges and maxima for the same samples as a mean or median are shown on that row.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Determination of Geographical and Seasonal Variations of Heavy Metals in Swordfish (Xiphias gladius) and Yellowfin Tuna (Thunnus albacares)International Journal of Current Science Research and ReviewRead source →3Assessment of metal levels in foodstuffs from the Region of Valencia (Spain)Toxicology Reports 5 (2018) 654-670Read source →4Heavy metals content in fresh tuna and swordfish caught from Hindian and Pacific Oceans: Health risk assessment of dietary exposureVeterinary WorldRead source →5Determination of toxic elements (mercury, cadmium, lead, tin and arsenic) in fish and shellfish samples. Risk assessment for the consumersEnvironment InternationalRead source →6Health Risk Assessment of Some Heavy Metals from Canned Tuna and Fish in Tijuana, MexicoHealth ScopeRead source → Monitoring medians are HMI calculations from individual submissions; non-detects remain intervals between zero and the reporting limit and are never read as zero.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
68 rows can be rated against an HMI reference for the same form and basis, 0 rows have a direct same-study comparison, and the rest stay unrated with the reason recorded. 4 values from 3 sources failed a check against their own source and are shown but not compared.7Kandungan Logam Berat Merkuri Pada Ikan Tuna (Yellowfin dan Bigeye) dan Tuna-like (Swordfish) Hasil Tangkapan dari Samudera Hindia dan Samudera PasifikJurnal Pascapanen dan Bioteknologi Kelautan dan PerikananRead source →8Species-specific mercury speciation in billfishes and itsPeer-reviewed articleRead source →9Risk assessment of mercury and methyl mercury intake via sardine and swordfish consumption in AlgeriaJournal of the Hellenic Veterinary Medical SocietyRead source →
Comparison methods and scope
Each row is one statistic a source reports for one form of swordfish, group and metal; percentiles, ranges and maxima reported for the same samples as a mean or median are shown on that row. Different forms and preparation states are kept apart, and dry-weight results never share a reference with as-sold or fresh-weight results. Ratings place a result against an HMI reference built from monitoring results and ordinary-setting medians for the same form and basis. Same-study contrasts compare a contaminated or treated site with its control, targeted with random sampling, a prepared form with the unprocessed one, or one group of a study with the median of its other groups. Held rows failed a check against their own source and are shown but not compared.
First displayed analyte: Lead: 18 findings from 7 sources. Each row retains its statistic and measurement basis.
Filter findings
142 of 142 findings · 17 analytes
About this table
| Food form | Collection scope | Finding (µg/kg) | Comparison | Evidence |
|---|---|---|---|---|
15 findings · 7 studies · 3 spread figures folded in | ||||
| Swordfish, as soldWHO GEMS/Food | EURO2003–2019 | median. | ||
| Swordfish, as soldWHO GEMS/Food | EURO2003–2019 | median. | ||
| Swordfish, as soldWHO GEMS/Food | PAHO2008–2017 | median. | ||
| Swordfish, as soldWHO GEMS/Food | SEARO2011–2012 | median. | ||
| Swordfish, as soldDASU et al. 2022 | export-company secondary data, all samples2015–2017 | not detected. | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | mean.Same samples: 3 µg/kg (minimum); 31.5 µg/kg (maximum) | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | min. | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | max. | ||
| Swordfish, as soldOktariani et al. 2023 | Indian Ocean, FAO zone 572012–2016 | range. | ||
| Swordfish, as soldOktariani et al. 2023 | Pacific Ocean, FAO zone 712012–2016 | range. | ||
| Swordfish, as soldOlmedo et al. 2013 | Fresh Swordfish (Galicia, Spain)2009–2010 | not detected. | ||
| Swordfish, as soldOlmedo et al. 2013 | fresh, origin Galicia, Spain2009–2010 | median.Same samples: 64 µg/kg (percentile) | ||
| Swordfish, as soldOlmedo et al. 2013 | fresh, origin Galicia, Spain2009–2010 | percentile. | ||
| Swordfish, as soldOlmedo et al. 2013 | fresh, origin Galicia, Spain2009–2010 | percentile. | ||
| Swordfish, as soldRodriguez-Mendivil et al. 2019 | all samples2016 | mean. | ||
| Swordfish, as soldRodriguez-Mendivil et al. 2019 | Fresh Swordfish2016 | range. | ||
| Swordfish, as soldSmolikova et al. 2016 | one batch of this species (batch not identified in text)2015–2016 | sample value. | ||
| Swordfish, as soldSmolikova et al. 2016 | Swordfish IX2015–2016 | mean. | ||
14 findings · 7 studies · 7 spread figures folded in | ||||
| Swordfish, as soldWHO GEMS/Food | EURO2004–2006 | median. | ||
| Swordfish, as soldWHO GEMS/Food | EURO2005–2006 | median. | ||
| Swordfish, as soldWHO GEMS/Food | EURO2003–2019 | median. | ||
| Swordfish, as soldWHO GEMS/Food | EURO2005–2006 | median. | ||
| Swordfish, as soldWHO GEMS/Food | EURO2004–2019 | median. | ||
| Swordfish, as soldDASU et al. 2022 | export-company secondary data, all samples2015–2017 | not detected. | ||
| Swordfish, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2009 | all samples (EU Member States and others, 2003-2007)2003–2007 | median. | ||
| Swordfish, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2009 | all samples (EU Member States and others, 2003-2007)2003–2007 | mean.Same samples: 399 µg/kg (maximum); 8 µg/kg (percentile); 228 µg/kg (percentile) | ||
| Swordfish, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2009 | all samples (EU Member States and others, 2003-2007)2003–2007 | max. | ||
| Swordfish, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2009 | all samples (EU Member States and others, 2003-2007)2003–2007 | percentile. | ||
| Swordfish, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2009 | all samples (EU Member States and others, 2003-2007)2003–2007 | percentile. | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | mean.Same samples: 38.5 µg/kg (minimum); 168 µg/kg (maximum) | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | min. | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | max. | ||
| Swordfish, as soldOktariani et al. 2023 | Indian Ocean, FAO zone 572012–2016 | range. | ||
| Swordfish, as soldOktariani et al. 2023 | Pacific Ocean, FAO zone 712012–2016 | range. | ||
| Swordfish, as soldOlmedo et al. 2013 | fresh, origin Galicia, Spain2009–2010 | median.Same samples: 2 µg/kg (percentile); 60 µg/kg (percentile) | ||
| Swordfish, as soldOlmedo et al. 2013 | fresh, origin Galicia, Spain2009–2010 | percentile. | ||
| Swordfish, as soldOlmedo et al. 2013 | fresh, origin Galicia, Spain2009–2010 | percentile. | ||
| Swordfish, as soldRodriguez-Mendivil et al. 2019 | all samples2016 | mean. | ||
| Swordfish, as soldRodriguez-Mendivil et al. 2019 | Fresh Swordfish2016 | range. | ||
8 findings · 4 studies · 4 spread figures folded in | ||||
| Swordfish, as soldWHO GEMS/Food | EURO2011–2015 | median. | ||
| Swordfish, as soldWHO GEMS/Food | EURO2014 | median. | ||
| Swordfish, as soldWHO GEMS/Food | EURO2014–2023 | median. | ||
| Swordfish, as soldWHO GEMS/Food | EURO2016 | median. | ||
| Swordfish, as soldWHO GEMS/Food | EURO2014–2017 | median. | ||
| Swordfish, as soldDASU et al. 2022 | export-company secondary data, all samples2015–2017 | not detected. | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | mean.Same samples: 944 µg/kg (minimum); 1,970 µg/kg (maximum) | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | min. | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | max. | ||
| Swordfish, as soldOlmedo et al. 2013 | fresh, origin Galicia, Spain2009–2010 | median.Same samples: 10 µg/kg (percentile); 910 µg/kg (percentile) | ||
| Swordfish, as soldOlmedo et al. 2013 | fresh, origin Galicia, Spain2009–2010 | percentile. | ||
| Swordfish, as soldOlmedo et al. 2013 | fresh, origin Galicia, Spain2009–2010 | percentile. | ||
3 findings · 2 studies · 2 spread figures folded in | ||||
| Swordfish, as soldWHO GEMS/Food | EURO2017–2023 | median. | ||
| Swordfish, as soldWHO GEMS/Food | EURO2017 | median. | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | mean.Same samples: 4.1 µg/kg (minimum); 14 µg/kg (maximum) | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | min. | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | max. | ||
2 findings · 1 study | ||||
| Swordfish, as soldWHO GEMS/Food | EURO2021 | median. | ||
| Swordfish, as soldWHO GEMS/Food | EURO2017 | median. | ||
50 findings · 19 studies · 17 spread figures folded in | ||||
| Swordfish, as soldWHO GEMS/Food | EURO2005–2020 | median. | ||
| Swordfish, as soldWHO GEMS/Food | EURO2006–2017 | median. | ||
| Swordfish, as soldWHO GEMS/Food | PAHO2007–2020 | median. | ||
| Swordfish, as soldWHO GEMS/Food | WPRO2005–2014 | median. | ||
| Swordfish, as soldauthors 2021 | demersal-pelagic fish, Apulian retail purchase2019 | sample value. | ||
| Swordfish, as soldauthors 2023 | Pacific and Indian Ocean originCollection date unreported | mean. | ||
| Swordfish, as soldauthors 2025 | New Caledonia (Pacific)2013–2022 | sample value. | ||
| Swordfish, as soldauthors 2025 | Reunion Island (Indian Ocean)2013–2022 | mean. | ||
| Swordfish, as soldauthors 2025 | Seychelles (Indian Ocean)2013–2022 | mean. | ||
| Swordfish, as soldauthors 2025 | South Africa (Indian Ocean)2013–2022 | mean. | ||
| Swordfish, as soldauthors 2025 | Swordfish, Indian Ocean, Reunion Islands2013–2022 | range. | ||
| Swordfish, as soldauthors 2025 | Swordfish, Indian Ocean, Seychelles2013–2022 | range. | ||
| Swordfish, as soldauthors 2025 | Swordfish, Indian Ocean, South Africa2013–2022 | range. | ||
| Swordfish, as soldBlanco et al. 2023 | all years 2011-2017, THg measurements2011–2017 | median.Same samples: 70–2,700 µg/kg (range) | ||
| Swordfish, as soldBlanco et al. 2023 | all years 2011-2017, THg measurements2011–2017 | range. | ||
| Swordfish, as soldBlanco et al. 2023 | sampling year 20112011–2017 | median. | ||
| Swordfish, as soldBlanco et al. 2023 | sampling year 20132011–2017 | median. | ||
| Swordfish, as soldBlanco et al. 2023 | sampling year 20172011–2017 | median. | ||
| Swordfish, as soldChristian et al. 2024 | all samples, family2005–2023 | geometric mean. | ||
| Swordfish, as soldChristian et al. 2024 | Swordfishes (Xiphiidae)2005–2023 | range. | ||
| Swordfish, as soldGarofalo et al. 2025 | all samples (marine fish species group)2014–2023 | median. | ||
| Swordfish, as soldGarofalo et al. 2025 | all samples (marine fish species group)2014–2023 | mean.Same samples: 2,900 µg/kg (maximum); 1,700 µg/kg (percentile); 2,400 µg/kg (percentile) | ||
| Swordfish, as soldGarofalo et al. 2025 | all samples (marine fish species group)2014–2023 | max. | ||
| Swordfish, as soldGarofalo et al. 2025 | all samples (marine fish species group)2014–2023 | percentile. | ||
| Swordfish, as soldGarofalo et al. 2025 | all samples (marine fish species group)2014–2023 | percentile. | ||
| Swordfish, as soldGarofalo et al. 2025 | samples exceeding the 1 mg/kg ML2014–2023 | mean. | ||
| Swordfish, as soldGarofalo et al. 2025 | Swordfish, non-compliant samples2014–2023 | range. | ||
| Swordfish, as soldHarding et al. 2018 | outer Bay of Fundy / Gulf of Maine (pelagic)2000–2003 | median. | ||
| Swordfish, as soldHarding et al. 2018 | outer Bay of Fundy / Gulf of Maine (pelagic)2000–2003 | mean.Same samples: 428–3,230 µg/kg (range) | ||
| Swordfish, as soldHarding et al. 2018 | outer Bay of Fundy / Gulf of Maine (pelagic)2000–2003 | range. | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | mean.Same samples: 1,090 µg/kg (minimum); 2,290 µg/kg (maximum) | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | min. | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | max. | ||
| Swordfish, as soldMehouel et al. 2019 | Algiers coast2017 | mean. | ||
| Swordfish, as soldMehouel et al. 2019 | all samples (3 Algerian coasts)2017 | mean. | ||
| Swordfish, as soldMehouel et al. 2019 | Bejaia coast2017 | mean. | ||
| Swordfish, as soldMehouel et al. 2019 | Oran coast2017 | mean. | ||
| Swordfish, as soldOktariani et al. 2023 | Indian Ocean, FAO zone 572012–2016 | range. | ||
| Swordfish, as soldOktariani et al. 2023 | Pacific Ocean, FAO zone 712012–2016 | range. | ||
| Swordfish, as soldOlmedo et al. 2013 | fresh, origin Galicia, Spain2009–2010 | median.Same samples: 177 µg/kg (percentile); 1,230 µg/kg (percentile) | ||
| Swordfish, as soldOlmedo et al. 2013 | fresh, origin Galicia, Spain2009–2010 | percentile. | ||
| Swordfish, as soldOlmedo et al. 2013 | fresh, origin Galicia, Spain2009–2010 | percentile. | ||
| Swordfish, as soldRodriguez-Mendivil et al. 2019 | all samples2016 | mean. | ||
| Swordfish, as soldRodriguez-Mendivil et al. 2019 | Fresh Swordfish2016 | range. | ||
| Swordfish, as soldWatanabe et al. 2017 | all samples of this species group2014–2015 | median. | ||
| Swordfish, as soldWatanabe et al. 2017 | all samples of this species group2014–2015 | mean.Same samples: 1,240 µg/kg (minimum); 1,880 µg/kg (maximum) | ||
| Swordfish, as soldWatanabe et al. 2017 | all samples of this species group2014–2015 | min. | ||
| Swordfish, as soldWatanabe et al. 2017 | all samples of this species group2014–2015 | max. | ||
| Swordfish, as soldYamashita 2024 | all samples2022–2023 | median.Same samples: 70 µg/kg (minimum); 2,190 µg/kg (maximum) | ||
| Swordfish, as soldYamashita 2024 | all samples2022–2023 | min. | ||
| Swordfish, as soldYamashita 2024 | all samples2022–2023 | max. | ||
| Swordfish, as soldYamashita 2024 | all samples (25th percentile)2022–2023 | percentile. | ||
| Swordfish, as soldYamashita 2024 | all samples (75th percentile)2022–2023 | percentile. | ||
| Swordfish, as soldYamashita 2024 | single specimen2022–2023 | sample value. | ||
| Swordfish, as soldCommittee on Toxicity of Chemicals in Food 2004 | 2002 FSA UK survey, imported fish/shellfish and UK farmed fish2002Basis not stated | mean. | ||
| Swordfish, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2012 | EU occurrence data2004–2011Basis not stated | median. | ||
| Swordfish, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2012 | EU occurrence data2004–2011Basis not stated | mean.Same samples: 6,760 µg/kg (maximum); 3,300 µg/kg (percentile); 4,500 µg/kg (percentile); 5,300 µg/kg (percentile) | ||
| Swordfish, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2012 | EU occurrence data2004–2011Basis not stated | max. | ||
| Swordfish, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2012 | EU occurrence data2004–2011Basis not stated | percentile. | ||
| Swordfish, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2012 | EU occurrence data2004–2011Basis not stated | percentile. | ||
| Swordfish, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2012 | EU occurrence data2004–2011Basis not stated | percentile. | ||
| Swordfish, as soldHandayani et al. 2019 | all groups, lowest group mean2012–2017Basis not stated | mean. | ||
| Swordfish, as soldHandayani et al. 2019 | Indian Ocean, highest weight group2012–2017Basis not stated | mean. | ||
| Swordfish, as soldHandayani et al. 2019 | Pacific Ocean (Bitung)2012–2017Basis not stated | range. | ||
| Swordfish, as soldHandayani et al. 2019 | Pacific Ocean (Bitung), highest group mean2012–2017Basis not stated | max. | ||
| Swordfish, as soldRalston et al. 2014 | all samples1977–1978Basis not stated | mean. | ||
| Swordfish, as soldWatanabe et al. 2017 | Swordfish2014–2015Basis not stated | range. | ||
5 findings · 2 studies | ||||
| Swordfish, peeled or fleshMehouel et al. 2019 | swordfish algiers2017 | range. | ||
| Swordfish, peeled or fleshMehouel et al. 2019 | swordfish all2017 | range. | ||
| Swordfish, peeled or fleshMehouel et al. 2019 | swordfish bejaia2017 | range. | ||
| Swordfish, peeled or fleshMehouel et al. 2019 | swordfish oran2017 | range. | ||
| Swordfish, peeled or fleshBlanco et al. 2023 | Pez espada/emperador 2011-20172011–2017Basis not stated | mean. | ||
24 findings · 10 studies · 6 spread figures folded in | ||||
| Swordfish, as soldWHO GEMS/Food | EURO2013–2017 | median. | ||
| Swordfish, as soldWHO GEMS/Food | WPRO2006–2014 | median. | ||
| Swordfish, as soldauthors 2021 | demersal-pelagic fish, Apulian retail purchase2019 | sample value. | ||
| Swordfish, as soldauthors 2023 | Pacific and Indian Ocean originCollection date unreported | mean. | ||
| Swordfish, as soldauthors 2025 | New Caledonia (Pacific)2013–2022 | sample value. | ||
| Swordfish, as soldauthors 2025 | Reunion Island (Indian Ocean)2013–2022 | mean. | ||
| Swordfish, as soldauthors 2025 | Seychelles (Indian Ocean)2013–2022 | mean. | ||
| Swordfish, as soldauthors 2025 | South Africa (Indian Ocean)2013–2022 | mean. | ||
| Swordfish, as soldauthors 2025 | Swordfish, Indian Ocean, Reunion Islands2013–2022 | range. | ||
| Swordfish, as soldauthors 2025 | Swordfish, Indian Ocean, Seychelles2013–2022 | range. | ||
| Swordfish, as soldauthors 2025 | Swordfish, Indian Ocean, South Africa2013–2022 | range. | ||
| Swordfish, as soldHarding et al. 2018 | outer Bay of Fundy / Gulf of Maine (pelagic)2000–2003 | median. | ||
| Swordfish, as soldHarding et al. 2018 | outer Bay of Fundy / Gulf of Maine (pelagic)2000–2003 | mean.Same samples: 249–1,190 µg/kg (range) | ||
| Swordfish, as soldHarding et al. 2018 | outer Bay of Fundy / Gulf of Maine (pelagic)2000–2003 | range. | ||
| Swordfish, as soldHsi et al. 2016 | Taipei City markets, 20142007–2014 | mean. | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | mean.Same samples: 627 µg/kg (minimum); 1,080 µg/kg (maximum) | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | min. | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | max. | ||
| Swordfish, as soldMehouel et al. 2019 | Algiers coast2017 | mean. | ||
| Swordfish, as soldMehouel et al. 2019 | all samples (3 Algerian coasts)2017 | mean. | ||
| Swordfish, as soldMehouel et al. 2019 | Bejaia coast2017 | mean. | ||
| Swordfish, as soldMehouel et al. 2019 | Oran coast2017 | mean. | ||
| Swordfish, as soldWatanabe et al. 2017 | all samples of this species group2014–2015 | median. | ||
| Swordfish, as soldWatanabe et al. 2017 | all samples of this species group2014–2015 | mean.Same samples: 1,020 µg/kg (minimum); 1,900 µg/kg (maximum) | ||
| Swordfish, as soldWatanabe et al. 2017 | all samples of this species group2014–2015 | min. | ||
| Swordfish, as soldWatanabe et al. 2017 | all samples of this species group2014–2015 | max. | ||
| Swordfish, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2012 | EU occurrence data2004–2011Basis not stated | median. | ||
| Swordfish, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2012 | EU occurrence data2004–2011Basis not stated | mean.Same samples: 1,080 µg/kg (maximum) | ||
| Swordfish, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2012 | EU occurrence data2004–2011Basis not stated | max. | ||
| Swordfish, as soldWatanabe et al. 2017 | Swordfish2014–2015Basis not stated | range. | ||
4 findings · 1 study | ||||
| Swordfish, peeled or fleshMehouel et al. 2019 | swordfish algiers2017 | range. | ||
| Swordfish, peeled or fleshMehouel et al. 2019 | swordfish all2017 | range. | ||
| Swordfish, peeled or fleshMehouel et al. 2019 | swordfish bejaia2017 | range. | ||
| Swordfish, peeled or fleshMehouel et al. 2019 | swordfish oran2017 | range. | ||
1 finding · 1 study | ||||
| Swordfish, as soldDASU et al. 2022 | Swordfish, June to September 2017, all stations2015–2017Basis not stated | range. | ||
3 findings · 2 studies · 2 spread figures folded in | ||||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | mean.Same samples: 10.8 µg/kg (minimum); 84.8 µg/kg (maximum) | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | min. | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | max. | ||
| Swordfish, as soldRodriguez-Mendivil et al. 2019 | all samples2016 | mean. | ||
| Swordfish, as soldRodriguez-Mendivil et al. 2019 | Fresh Swordfish2016 | range. | ||
1 finding · 1 study · 2 spread figures folded in | ||||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | mean.Same samples: 4.8 µg/kg (minimum); 18.4 µg/kg (maximum) | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | min. | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | max. | ||
1 finding · 1 study · 2 spread figures folded in | ||||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | mean.Same samples: 302 µg/kg (minimum); 506 µg/kg (maximum) | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | min. | ||
| Swordfish, as soldMarín et al. 2018 | Fish and seafood group, Region of Valencia TDS 2010-20112010–2011 | max. | ||
6 findings · 3 studies | ||||
| Swordfish, as soldauthors 2021 | demersal-pelagic fish, Apulian retail purchase2019 | sample value. | ||
| Swordfish, as soldauthors 2025 | New Caledonia (Pacific)2013–2022 | sample value. | ||
| Swordfish, as soldauthors 2025 | Reunion Island (Indian Ocean)2013–2022 | mean. | ||
| Swordfish, as soldauthors 2025 | Seychelles (Indian Ocean)2013–2022 | mean. | ||
| Swordfish, as soldauthors 2025 | South Africa (Indian Ocean)2013–2022 | mean. | ||
| Swordfish, as soldRalston et al. 2014 | all samples1977–1978Basis not stated | mean. | ||
1 finding · 1 study | ||||
| Swordfish, as soldauthors 2023 | Pacific and Indian Ocean originCollection date unreported | not detected. | ||
1 finding · 1 study | ||||
| Swordfish, as soldauthors 2023 | Pacific and Indian Ocean originCollection date unreported | mean. | ||
1 finding · 1 study | ||||
| Swordfish, as soldauthors 2023 | Pacific and Indian Ocean originCollection date unreported | not detected. | ||
1 finding · 1 study | ||||
| Swordfish, as soldauthors 2023 | Pacific and Indian Ocean originCollection date unreported | mean. | ||
1 finding · 1 study | ||||
| Swordfish, as soldauthors 2023 | Pacific and Indian Ocean originCollection date unreported | mean. | ||
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 swordfish Pb reference · Swordfish, as sold
Reference and scope
HMI swordfish Pb reference · Swordfish, as sold. Swordfish, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤4.35 | ≤20 | 25 |
| Alternative weighting | ≤4.35 | ≤20 | 25 |
37 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 35 | 33% |
| Olmedo et al. 2013 | 1 | 33% |
| Smolikova et al. 2016 | 1 | 33% |
Methods
HMI pools subgroup medians for swordfish, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
3 sampling families with different designs; none is a probability sample of world supply. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:swordfish-2d4e63234c29:6c53a842eede
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not 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 Cd reference · Swordfish, as sold
Reference and scope
HMI swordfish Cd reference · Swordfish, as sold. Swordfish, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 9 | 35.9 | 35.9 |
| Alternative weighting | 9 | 35.9 | 35.9 |
31 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 29 | 33% |
| EFSA Panel on Contaminants in the Food Chain (CONTAM) 2009 | 1 | 33% |
| Olmedo et al. 2013 | 1 | 33% |
Methods
HMI pools subgroup medians for swordfish, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
3 sampling families with different designs; none is a probability sample of world supply. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:swordfish-3c04fd7a34e5:3c7eaa467d1b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not 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 tAs reference · Swordfish, as sold
Reference and scope
HMI swordfish tAs reference · Swordfish, as sold. Swordfish, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 96 | 198 | 1040 |
| Alternative weighting | 96 | 198 | 1100 |
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% |
| Olmedo et al. 2013 | 1 | 50% |
Methods
HMI pools subgroup medians for swordfish, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
2 sampling families with different designs; none is a probability sample of world supply. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:swordfish-3ca625c93020:8b5f3d8a5ad0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not 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 iAs reference · Swordfish, as sold
Reference and scope
HMI swordfish iAs reference · Swordfish, as sold. Swordfish, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤20 | ≤20 |
| Alternative weighting | ≤10 | ≤20 | ≤20 |
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 swordfish, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
WHO GEMS/Food is the only compatible sampling family for swordfish, as sold on this basis in the completed swordfish ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:swordfish-a9d0ea9c2025:7d14f938537c
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not 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 DMA reference · Swordfish, as sold
Reference and scope
HMI swordfish DMA reference · Swordfish, as sold. Swordfish, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | 10–20 (bounded) | 20–30 (bounded) |
| Alternative weighting | ≤10 | 10–20 (bounded) | 20–30 (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 swordfish, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
WHO GEMS/Food is the only compatible sampling family for swordfish, as sold on this basis in the completed swordfish ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:swordfish-65cca039c484:cc78cab0c1c5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not 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 tHg reference · Swordfish, as sold
Reference and scope
HMI swordfish tHg reference · Swordfish, as sold. Swordfish, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 589 | 670 | 1030 |
| Alternative weighting | 589 | 670 | 1030 |
49 reference units; 9 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 38 | 11% |
| authors 2021 | 1 | 11% |
| authors 2025 | 1 | 11% |
| Blanco et al. 2023 | 3 | 11% |
| Garofalo et al. 2025 | 1 | 11% |
| Harding et al. 2018 | 1 | 11% |
| Olmedo et al. 2013 | 1 | 11% |
| Watanabe et al. 2017 | 1 | 11% |
| Yamashita 2024 | 2 | 11% |
Methods
HMI pools subgroup medians for swordfish, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
9 sampling families with different designs; none is a probability sample of world supply. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
- WHO GEMS/Food
- authors 2021
- authors 2025
- Blanco et al. 2023
- Garofalo et al. 2025
- Harding et al. 2018
- Olmedo et al. 2013
- Watanabe et al. 2017
- Yamashita 2024
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:swordfish-7e7159c86195:c8f23c6cc1bb
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not 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 MeHg reference · Swordfish, as sold
Reference and scope
HMI swordfish MeHg reference · Swordfish, as sold. Swordfish, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 550 | 628 | 1420 |
| Alternative weighting | 550 | 628 | 1420 |
12 reference units; 4 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 9 | 25% |
| authors 2021 | 1 | 25% |
| Harding et al. 2018 | 1 | 25% |
| Watanabe et al. 2017 | 1 | 25% |
Methods
HMI pools subgroup medians for swordfish, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
4 sampling families with different designs; none is a probability sample of world supply. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:swordfish-85f91de8165d:467317d97f94
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not 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 Se reference · Swordfish, as sold
Reference and scope
HMI swordfish Se reference · Swordfish, as sold. Swordfish, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 440 | 665 | 890 |
| Alternative weighting | 440 | 665 | 890 |
2 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| authors 2021 | 1 | 50% |
| authors 2025 | 1 | 50% |
Methods
HMI pools subgroup medians for swordfish, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
2 sampling families with different designs; none is a probability sample of world supply. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:swordfish-ae0707c06234:a914573d9706
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not 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 Se(IV) reference · Swordfish, as sold
Reference and scope
HMI swordfish Se(IV) reference · Swordfish, as sold. Swordfish, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤149 | ≤149 | ≤149 |
| Alternative weighting | ≤149 | ≤149 | ≤149 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| authors 2023 | 1 | 100% |
Methods
HMI pools subgroup medians for swordfish, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
authors 2023 is the only compatible sampling family for swordfish, as sold on this basis in the completed swordfish ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:swordfish-1acc5b6c2e03:be3acf02eb7d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not 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 SeCys reference · Swordfish, as sold
Reference and scope
HMI swordfish SeCys reference · Swordfish, as sold. Swordfish, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. 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 |
|---|---|---|
| authors 2023 | 1 | 100% |
Methods
HMI pools subgroup medians for swordfish, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
authors 2023 is the only compatible sampling family for swordfish, as sold on this basis in the completed swordfish ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:swordfish-4de9c6c549ec:ad88fc1e2c50
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is 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.
No findings match these filters. Change the selection or reset to show all source findings.
How metals reach swordfish
No study in the library compared swordfish from contaminated and ordinary settings, so the routes by which metals reach it are not measured here.
Which forms and regions measured lower
The HMI reference for lead in swordfish, as sold pools 37 subgroup units from 3 sampling families, with a median of below 20 µg/kg and a middle half spanning below 4.35 (lower quartile) and 25 µg/kg (upper quartile).1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →5Determination of toxic elements (mercury, cadmium, lead, tin and arsenic) in fish and shellfish samples. Risk assessment for the consumersEnvironment InternationalRead source →10Determination of heavy metals in fish productsMendelNet 2016: Proceedings of International PhD Students Conference, pp. 651-656Read source → For cadmium in swordfish, as sold, the reference median was 35.9 µg/kg, with a middle half from 9 to 35.9 µg/kg across 31 units.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →5Determination of toxic elements (mercury, cadmium, lead, tin and arsenic) in fish and shellfish samples. Risk assessment for the consumersEnvironment InternationalRead source →11Scientific Opinion of the Panel on Contaminants in the Food Chain on a request from the European Commission on cadmium in foodThe EFSA JournalRead source → For total arsenic in swordfish, as sold, the reference median was 198 µg/kg, with a middle half from 96 to 1,040 µg/kg across 18 units.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →5Determination of toxic elements (mercury, cadmium, lead, tin and arsenic) in fish and shellfish samples. Risk assessment for the consumersEnvironment InternationalRead source →
Among GEMS/Food reporting regions, swordfish, as sold had the lowest cadmium subgroup median in EURO (41.5 µg/kg) and the highest in EURO (53 µg/kg); reporting regions are markets, not growing areas.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → For total arsenic, the lowest regional median was in EURO (670 µg/kg) and the highest in EURO (1,100 µg/kg).1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → For total mercury, the lowest regional median was in WPRO (403 µg/kg) and the highest in PAHO (995 µg/kg).1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
Targeted swordfish, as sold samples in EURO had cadmium lower at 30 µg/kg, against 41.5 µg/kg for EURO in the same study.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → In another study, targeted swordfish, as sold samples in EURO had total arsenic higher at 2,300 µg/kg, against 854 µg/kg for EURO in the same study.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
Processing, cooking and preparation
No processing study for metals in this food is in the library yet.
Mitigation for swordfish
Lot testing against the applicable limit is the check that can be verified.
No measured way to lower metals in this food is in the library yet.
Trade-offs and limits of controls
Metals do not move together, so a lot that passes a lead limit says little about cadmium, arsenic or nickel unless those are tested as well.
Testing swordfish for metals
Results depend on the method and its reporting limit. Reporting limits for lead ranged from 4.35 µg/kg (Olmedo et al. 2013) to 200 µg/kg (WHO GEMS/Food), so a non-detect from a less sensitive method says much less.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →5Determination of toxic elements (mercury, cadmium, lead, tin and arsenic) in fish and shellfish samples. Risk assessment for the consumersEnvironment InternationalRead source → Reporting limits for cadmium ranged from 0.8 µg/kg (WHO GEMS/Food) to 60 µg/kg (WHO GEMS/Food), so a non-detect from a less sensitive method says much less.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → Reporting limits for total arsenic ranged from 4.3 µg/kg (WHO GEMS/Food) to 50 µg/kg (WHO GEMS/Food), so a non-detect from a less sensitive method says much less.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
A useful lot result names the form, the basis and a quantification limit well below the limit that applies.
Buying and verifying swordfish
No maximum level for metals in swordfish was verified from primary text for this page; buyers should confirm the limit that applies in the destination market.
Exposure from swordfish
No source in the library converted swordfish concentrations into a verified estimate of intake for a defined population. Concentrations describe the food, not individual risk.
Evidence review and remaining gaps
Every source record that names swordfish was decided on its content: 23 occurrence extracted, 23 records in all. The occurrence table renders every extracted result; held values remain visible with their reason.
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.
Swordfish FAQs
What heavy metals are found in swordfish?
The library reports lead, cadmium, total arsenic, inorganic arsenic, dimethylarsinic acid, total mercury, methylmercury, mercury, chromium, tin, Cu, Se, Se(IV), Se(VI), SeCys, SeMet and tSe in swordfish, most often lead, cadmium and total arsenic.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Determination of Geographical and Seasonal Variations of Heavy Metals in Swordfish (Xiphias gladius) and Yellowfin Tuna (Thunnus albacares)International Journal of Current Science Research and ReviewRead source →3Assessment of metal levels in foodstuffs from the Region of Valencia (Spain)Toxicology Reports 5 (2018) 654-670Read source →4Heavy metals content in fresh tuna and swordfish caught from Hindian and Pacific Oceans: Health risk assessment of dietary exposureVeterinary WorldRead source → WHO GEMS/Food submissions reported lead in swordfish, as sold from 839 results in 3 reporting regions, with subgroup medians below 20 µg/kg, mostly non-detects.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
Which regions report the lowest levels in swordfish?
Among GEMS/Food reporting regions, swordfish, as sold had the lowest cadmium subgroup median in EURO (41.5 µg/kg) and the highest in EURO (53 µg/kg); reporting regions are markets, not growing areas.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → For total arsenic, the lowest regional median was in EURO (670 µg/kg) and the highest in EURO (1,100 µg/kg).1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
How much of the arsenic in swordfish is inorganic?
Inorganic arsenic, the more toxic form, was measured in 5 results from 2 sources, far fewer than total arsenic.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →3Assessment of metal levels in foodstuffs from the Region of Valencia (Spain)Toxicology Reports 5 (2018) 654-670Read source → Marín et al. 2018 reported inorganic arsenic at 9.7 µg/kg (mean) in swordfish, as sold from Fish and seafood group, Region of Valencia TDS 2010-2011.3Assessment of metal levels in foodstuffs from the Region of Valencia (Spain)Toxicology Reports 5 (2018) 654-670Read 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.
- GEMS/Food Contaminants database heavy-metal exportsDataset
- Determination of Geographical and Seasonal Variations of Heavy Metals in Swordfish (Xiphias gladius) and Yellowfin Tuna (Thunnus albacares)Peer-reviewed
- Assessment of metal levels in foodstuffs from the Region of Valencia (Spain)Peer-reviewed
- Heavy metals content in fresh tuna and swordfish caught from Hindian and Pacific Oceans: Health risk assessment of dietary exposurePeer-reviewed
- Determination of toxic elements (mercury, cadmium, lead, tin and arsenic) in fish and shellfish samples. Risk assessment for the consumersPeer-reviewed
- Health Risk Assessment of Some Heavy Metals from Canned Tuna and Fish in Tijuana, MexicoPeer-reviewed
- Kandungan Logam Berat Merkuri Pada Ikan Tuna (Yellowfin dan Bigeye) dan Tuna-like (Swordfish) Hasil Tangkapan dari Samudera Hindia dan Samudera PasifikPeer-reviewed
- Species-specific mercury speciation in billfishes and itsPeer-reviewed
- Risk assessment of mercury and methyl mercury intake via sardine and swordfish consumption in AlgeriaPeer-reviewed
- Determination of heavy metals in fish productsConference
- Scientific Opinion of the Panel on Contaminants in the Food Chain on a request from the European Commission on cadmium in foodGovernment
Sources
Browse Swordfish 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 swordfish record in the library: 23 occurrence sources, references by form and basis, same-study contrasts.
