Inorganic arsenic is the metal to check in seaweed: hijiki carries about 47–77 mg/kg as sold, while nori, wakame and most kombu measure about 0.1–0.3 mg/kg.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →3Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaFood Standards Australia New Zealand (FSANZ), Survey reportRead source →
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Metals of concern:
Inorganic arsenic in hijiki and oarweed; cadmium in laver and wakame; lead and mercury usually low.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →
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Main drivers:
Seaweed type and kelp species, growing water and tissue age, and preparation.4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →6Evidence of elevated heavy metals concentrations in wild and farmed sugar kelp (Saccharina latissima) in New EnglandScientific ReportsRead source →7Decrease of arsenic in edible brown algae Hijikia fusiforme by the cooking processApplied Organometallic ChemistryRead source →
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Practical framing:
Avoid hijiki, name the kelp species, and ask for inorganic arsenic and cadmium results.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →
Seaweed overview
Inorganic arsenic decides most seaweed questions, and it depends far more on the type of seaweed than on where it was bought. Hijiki is the clear outlier: nine retail hijiki products in the United Kingdom averaged 77 mg/kg inorganic arsenic as sold, and WHO GEMS/Food hijiki submissions had a median of 47 mg/kg (10 results, 2010–2024).1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → Nori, wakame and most kombu sold in Australia and Europe measured about 0.1–0.3 mg/kg, two to three orders of magnitude lower on the same dried-as-sold basis.3Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaFood Standards Australia New Zealand (FSANZ), Survey reportRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →
Total arsenic is high in almost every seaweed but is mostly organic arsenosugars, so a total arsenic result cannot stand in for inorganic arsenic.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →8Arsenic speciation in edible alga samples by microwave-assisted extraction and high performance liquid chromatography coupled to atomic fluorescence spectrometryAnalytica Chimica ActaRead source →9Concentrations and speciation of arsenic in New England seaweed species harvested for food and agricultureChemosphereRead source → Dried kombu in GEMS/Food had a median of 47 mg/kg total arsenic while the same dried-kombu category had a median of 0.23 mg/kg inorganic arsenic.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → Two kelps break the pattern: Norwegian oarweed (Laminaria digitata) had a median of 21 mg/kg inorganic arsenic dry weight, against 0.037 mg/kg in tangle (Laminaria hyperborea) from the same monitoring programme.4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →
Cadmium is the second metal to watch and it ranks the types differently. In European monitoring, dried laver (nori) averaged 1.68 mg/kg cadmium and dried wakame 1.28 mg/kg, against 0.46 mg/kg in dried kombu, so the lowest inorganic arsenic types are not the lowest cadmium types.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source → Lead and mercury are usually low: most dried-seaweed mercury results in GEMS/Food were below a 50 µg/kg detection limit, and dried nori lead had a median of about 0.14 mg/kg.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
For buyers, the supported priorities are to avoid hijiki or require an inorganic arsenic result for it, to specify the kelp species, and to ask for a cadmium result on nori, wakame and laver products.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source → Soaking and boiling remove a large share of arsenic from hijiki and other brown seaweeds into the water, which must then be discarded, but they leave a measurable residue and do little for cadmium.7Decrease of arsenic in edible brown algae Hijikia fusiforme by the cooking processApplied Organometallic ChemistryRead source →10Estimation of Arsenic Bioaccessibility in Edible Seaweed by an in Vitro Digestion MethodJournal of Agricultural and Food ChemistryRead source →11Tracing the natural and anthropogenic influence on the trace elemental chemistry of estuarine macroalgae and the implications for human consumptionScience of the Total EnvironmentRead source →12Pulsed electric field processing as an alternative to warm water treatment for the reduction of potentially toxic elements in Saccharina latissimaJournal of Applied PhycologyRead source →
Seaweed identity and scope
This page covers edible marine macroalgae: brown seaweeds such as kombu and other kelps (Laminaria, Saccharina), wakame (Undaria), hijiki (Sargassum fusiforme), arame and the wracks (Fucus, Ascophyllum); red seaweeds such as nori and laver (Porphyra, Pyropia), dulse and Irish moss; and green seaweeds such as sea lettuce (Ulva).4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source → Results stay separate by seaweed type because types differ systematically, and kelp species are named where the source names them.4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →13High proportions of inorganic arsenic in Laminaria digitata but not in Ascophyllum nodosum samples from IrelandChemosphereRead source →
Spirulina, chlorella and other microalgae or cyanobacteria are not seaweed and are excluded, as are foods that only contain seaweed, such as sushi rolls, seaweed snacks mixed with other ingredients, dashi broth and seasoning salts, unless the seaweed itself was measured.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →14Intake of food supplements based on algae or cyanobacteria may pose a health risk due to elevated concentrations of arsenic speciesFood Additives & Contaminants: Part ARead source → Kelp supplements made from dried seaweed are shown as their own form and are never pooled with seaweed foods.14Intake of food supplements based on algae or cyanobacteria may pose a health risk due to elevated concentrations of arsenic speciesFood Additives & Contaminants: Part ARead source →15Improved Arsenic Speciation Analysis for Extracts of Commercially Available Edible Marine Algae Using HPLC-ES-MS/MSJournal of Agricultural and Food Chemistry 54(18):6507-6519Read source →
The basis matters as much as the type. Fresh seaweed is roughly 85% water, so a fresh-weight concentration is several times lower than a dry-weight one for the same plant, and Australia and New Zealand express their seaweed limit at 85% hydration.3Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaFood Standards Australia New Zealand (FSANZ), Survey reportRead source →16Australia New Zealand Food Standards Code - Schedule 19 - Maximum levels of contaminants and natural toxicantsFederal Register of Legislation, Authorised Version F2024C00908Read source → This page keeps dry-weight laboratory results, dried products as sold, fresh or wet results and prepared (soaked or cooked) results apart, and never converts between them without the measured moisture of that sample.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →
Heavy metal contamination profile of seaweed
The table holds every seaweed result extracted from 78 sources: WHO GEMS/Food monitoring summarised by seaweed type, product form, basis and WHO region, agency reports and published surveys.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →3Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaFood Standards Australia New Zealand (FSANZ), Survey reportRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source → Each row is one statistic a source reports for one seaweed group and metal, so a mean, a median and individual samples appear as separate rows.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →6Evidence of elevated heavy metals concentrations in wild and farmed sugar kelp (Saccharina latissima) in New EnglandScientific ReportsRead source →17Chemical contaminant levels in edible seaweeds of the Salish Sea and implications for their consumptionPLOS ONERead source → Total arsenic, inorganic arsenic and dimethylarsinic acid are separate metals in the table, and other arsenic species are kept in the evidence records rather than shown as rows.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →8Arsenic speciation in edible alga samples by microwave-assisted extraction and high performance liquid chromatography coupled to atomic fluorescence spectrometryAnalytica Chimica ActaRead source →
Ratings place a mean, median or single result against a pooled HMI seaweed reference for the same metal and basis, built from every compatible sampling family: GEMS/Food subgroup medians, individual sample values and published subgroup medians.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →6Evidence of elevated heavy metals concentrations in wild and farmed sugar kelp (Saccharina latissima) in New EnglandScientific ReportsRead source →17Chemical contaminant levels in edible seaweeds of the Salish Sea and implications for their consumptionPLOS ONERead source → All seaweed types share one reference per basis, so a High rating for hijiki inorganic arsenic means high among seaweeds, not high against a safety threshold.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → Non-detects stay as intervals, and 54 rows whose values could not be reconciled with their own papers are shown with the reason and not compared.18Human Exposure to Toxic Metals (Cd, Pb, Hg) and Nitrates (NO3−) from Seaweed ConsumptionApplied SciencesRead source →19Effect of thermal processing on toxic heavy metals in edible seaweeds of Gulf of Mannar and their health risk assessmentRegional Studies in Marine ScienceRead source →20Elevated Concentrations of Metal(loids) in Seaweed and the Concomitant Exposure to HumansFoodsRead source →
Comparison methods and scope
Each row is one statistic a source reports for one seaweed group and metal; a mean, median and range from the same samples are separate rows. Total and inorganic arsenic are separate metals. Dry-weight, dried-as-sold and wet results are never mixed. Ratings place a reported mean, median or sample result against a pooled HMI reference for the same metal and basis, built from every compatible seaweed sampling family. Same-study contrasts compare a subgroup with its own study total. Held rows failed a check against their own paper and are shown but not compared.
First displayed analyte: Inorganic arsenic: 652 findings from 32 sources. Each row retains its statistic and measurement basis.
Filter findings
3866 of 3866 findings · 11 analytes
About this table
| Food form | Collection scope | Finding (µg/kg) | Comparison | Evidence |
|---|---|---|---|---|
427 findings · 25 studies · 11 spread figures folded in | ||||
| Hijiki · driedWHO GEMS/Food | WHO region EURO; random sampling2018–2020Dried product as sold | median. | ||
| Hijiki · driedWHO GEMS/Food | WHO region WPRO; random sampling2015–2024Dried product as sold | median. | ||
| Hijiki · driedWHO GEMS/Food | WHO region WPRO; targeted sampling2010Dried product as sold | median. | ||
| Hijiki · driedDuinker et al. 2020 | Sargassum fusiforme2014–2019 | sample value. | ||
| Hijiki · driedEFSA et al. 2021 | Sea weeds2013–2018Basis not stated | mean. | ||
| Hijiki · driedEFSA et al. 2021 | Sea weeds2013–2018Basis not stated | sample value. | ||
| Hijiki · driedEFSA et al. 2021 | Sea weeds2013–2018Basis not stated | sample value. | ||
| Hijiki · driedEFSA et al. 2021 | Sea weeds2013–2018Basis not stated | sample value. | ||
| Hijiki · driedFSANZ 2010 seaweed survey | Hijiki2010–2013Dried product as sold | sample value. | ||
| Hijiki · driedFSANZ 2010 seaweed survey | Hijiki2010–2013Recalculated to 85% hydration | sample value. | ||
| Hijiki · driedFSANZ 2010 seaweed survey | Sargassum fusiforme2010–2013Dried product as sold | sample value. | ||
| Hijiki · driedAlmela et al. 2002 | retail product 16Collection date unreported | sample value. | ||
| Hijiki · driedAlmela et al. 2002 | retail product 17Collection date unreported | sample value. | ||
| Hijiki · driedAlmela et al. 2002 | retail product 18Collection date unreported | sample value. | ||
| Hijiki · driedBralatei et al. 2017 | HijikiCollection date unreportedBasis not stated | range. | ||
| Hijiki · driedBralatei et al. 2017 | HijikiCollection date unreportedBasis not stated | range. | ||
| Hijiki · driedGarcía et al. 2006 | Hijiki, Spanish marketCollection date unreportedBasis not stated | sample value. | ||
| Hijiki · driedGarcía-Salgado et al. 2012 | Hijiki, JapanCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2010 | dried hijikiCollection date unreportedBasis not stated | sample value. | ||
| Hijiki · driedLaparra et al. 2003 | Hizikia fusiforme rawCollection date unreported | sample value. | ||
| Hijiki · driedMcSheehy et al. 2000 | sample BCollection date unreportedDried product as sold | sample value. | ||
| Hijiki · driedMcSheehy et al. 2000 | sample CCollection date unreportedDried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | mean.Same samples: 67,000–96,000 µg/kg (range) | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | range. | ||
| Hijiki · driedShimoda et al. 2010 | sample 1; China; unknown)Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 2Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 3Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 4Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 5Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 6Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 7Collection date unreported | sample value. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region EURO; random sampling2014–2023Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region EURO; targeted sampling2018–2019Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region WPRO; random sampling2015–2024Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region WPRO; targeted sampling2010Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region WPRO; targeted sampling2015 | median. | ||
| Kombu/kelp · driedDuinker et al. 2020 | Saccharina spp2014–2019 | mean.Same samples: 20–50 µg/kg (range) | ||
| Kombu/kelp · driedDuinker et al. 2020 | Saccharina spp2014–2019 | median. | ||
| Kombu/kelp · driedDuinker et al. 2020 | Saccharina spp2014–2019 | range. | ||
| Kombu/kelp · driedEFSA 2023 seaweed report | Kombu / Dried product2011–2022Dried product as sold | mean. | ||
| Kombu/kelp · driedEFSA 2023 seaweed report | Kombu / Dried product2011–2022Dried product as sold | mean. | ||
| Kombu/kelp · driedEFSA et al. 2021 | Kombu2013–2018Basis not stated | mean. | ||
| Kombu/kelp · driedEFSA et al. 2021 | Kombu2013–2018Basis not stated | mean. | ||
| Kombu/kelp · driedEFSA et al. 2021 | Kombu2013–2018Basis not stated | sample value. | ||
| Kombu/kelp · driedFSANZ 2010 seaweed survey | Kombu2010–2013Dried product as sold | mean. | ||
| Kombu/kelp · driedFSANZ 2010 seaweed survey | Kombu2010–2013Dried product as sold | sample value. | ||
| Kombu/kelp · driedFSANZ 2010 seaweed survey | Kombu2010–2013Dried product as sold | sample value. | ||
| Kombu/kelp · driedFSANZ 2010 seaweed survey | Kombu2010–2013Dried product as sold | sample value. | ||
| Kombu/kelp · driedFSANZ 2010 seaweed survey | Kombu2010–2013Dried product as sold | sample value. | ||
| Kombu/kelp · driedAlmela et al. 2002 | retail product 13Collection date unreported | sample value. | ||
| Kombu/kelp · driedAlmela et al. 2002 | retail product 14Collection date unreported | sample value. | ||
| Kombu/kelp · driedBralatei et al. 2017 | Laminaria digitata, IrelandCollection date unreportedBasis not stated | mean. | ||
| Kombu/kelp · driedBralatei et al. 2017 | Laminaria digitata, IrelandCollection date unreportedBasis not stated | mean. | ||
| Kombu/kelp · driedDíaz et al. 2012 | Lessonia nigrescens2003–2004 | mean. | ||
| Kombu/kelp · driedDíaz et al. 2012 | Macrocystis piryfera2003–2004 | mean. | ||
| Kombu/kelp · driedGarcía-Salgado et al. 2012 | Kombu, FranceCollection date unreported | sample value. | ||
| Kombu/kelp · driedGarcía-Salgado et al. 2012 | Kombu, JapanCollection date unreported | sample value. | ||
| Kombu/kelp · driedGarcía-Salgado et al. 2012 | Kombu, SpainCollection date unreported | sample value. | ||
| Kombu/kelp · driedGarcía-Salgado et al. 2012 | Laminaria, FranceCollection date unreported | sample value. | ||
| Kombu/kelp · driedLlorente-Mirandes et al. 2011 | Laminaria ochroleucaCollection date unreported | below LOD. | ||
| Kombu/kelp · driedLlorente-Mirandes et al. 2011 | Laminaria saccharinaCollection date unreported | below LOD. | ||
| Kombu/kelp · driedMatsumoto-Tanibuchi et al. 2019 | Dried kelpCollection date unreportedDried product as sold | below LOD. | ||
| Kombu/kelp · driedMcSheehy et al. 2000 | sample ECollection date unreportedDried product as sold | sample value. | ||
| Kombu/kelp · driedMcSheehy et al. 2000 | sample FCollection date unreportedDried product as sold | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | Laminaria digitataCollection date unreported | range. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | Laminaria digitata, site at 2.7° WCollection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | Laminaria japonicaCollection date unreported | range. | ||
| Kombu/kelp · driedRonan et al. 2017 | Laminaria digitata blades2015 | range. | ||
| Kombu/kelp · driedRonan et al. 2017 | Laminaria digitata2015 | range. | ||
| Kombu/kelp · driedRonan et al. 2017 | Laminaria digitata2015 | max. | ||
| Kombu/kelp · driedRose et al. 2007 | Kombu2003Dried product as sold | sample value. | ||
| Kombu/kelp · driedRose et al. 2007 | Kombu2003Dried product as sold | below LOD. | ||
| Kombu/kelp · driedRose et al. 2007 | Kombu2003Dried product as sold | below LOD. | ||
| Kombu/kelp · driedRose et al. 2007 | Kombu2003Dried product as sold | below LOD. | ||
| Kombu/kelp · driedRose et al. 2007 | Kombu2003Dried product as sold | below LOD. | ||
| Kombu/kelp · driedRose et al. 2007 | Kombu2003Dried product as sold | below LOD. | ||
| Kombu/kelp · driedRose et al. 2007 | Kombu2003Dried product as sold | below LOD. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Farmed; base of blade2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Farmed; distal tip2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Wild2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Wild2018–2021 | mean. | ||
| Kombu/kelp · driedSim et al. 2024 | L. digitata2020–2022 | mean. | ||
| Kombu/kelp · driedSim et al. 2024 | L. digitata2020–2022 | mean. | ||
| Kombu/kelp · driedSim et al. 2024 | S. latissima2020–2022 | mean. | ||
| Kombu/kelp · driedSim et al. 2024 | S. latissima2020–2022 | mean. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Agarum clathratum2012Basis not stated | below LOD. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Alaria esculenta2012Basis not stated | mean. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Laminaria digitata2012Basis not stated | mean. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Laminaria digitata2012Basis not stated | range. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Laminaria digitata2012Basis not stated | below LOD. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Laminaria longicruris2012Basis not stated | mean. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Saccharina latissima2012Basis not stated | below LOD. | ||
| Kombu/kelp · driedUnknown 2018 | sample 14Collection date unreportedBasis not stated | not detected. | ||
| Kombu/kelp · driedUnknown 2018 | sample 15Collection date unreportedBasis not stated | sample value. | ||
| Wakame · driedWHO GEMS/Food | WHO region EURO; random sampling2013–2023Dried product as sold | median. | ||
| Wakame · driedWHO GEMS/Food | WHO region EURO; targeted sampling2022Dried product as sold | median. | ||
| Wakame · driedWHO GEMS/Food | WHO region WPRO; random sampling2015–2024Dried product as sold | median. | ||
| Wakame · driedWHO GEMS/Food | WHO region WPRO; targeted sampling2010–2015Dried product as sold | median. | ||
| Wakame · driedWHO GEMS/Food | WHO region WPRO; targeted sampling2015 | median. | ||
| Wakame · driedDuinker et al. 2020 | Undaria pinnatifida2014–2019 | mean.Same samples: up to 60 µg/kg (range maximum) | ||
| Wakame · driedDuinker et al. 2020 | Undaria pinnatifida2014–2019 | median. | ||
| Wakame · driedDuinker et al. 2020 | Undaria pinnatifida2014–2019 | range. | ||
| Wakame · driedEFSA 2023 seaweed report | Wakame / Dried product2011–2022Dried product as sold | mean. | ||
| Wakame · driedEFSA 2023 seaweed report | Wakame / Dried product2011–2022Dried product as sold | mean. | ||
| Wakame · driedEFSA et al. 2021 | Wakame2013–2018Basis not stated | mean. | ||
| Wakame · driedEFSA et al. 2021 | Wakame2013–2018Basis not stated | mean. | ||
| Wakame · driedEFSA et al. 2021 | Wakame2013–2018Basis not stated | mean. | ||
| Wakame · driedFSANZ 2010 seaweed survey | Wakame2010–2013Dried product as sold | mean. | ||
| Wakame · driedFSANZ 2010 seaweed survey | Wakame2010–2013Dried product as sold | sample value. | ||
| Wakame · driedFSANZ 2010 seaweed survey | Wakame2010–2013Dried product as sold | sample value. | ||
| Wakame · driedFSANZ 2010 seaweed survey | Wakame2010–2013Dried product as sold | sample value. | ||
| Wakame · driedFSANZ 2010 seaweed survey | Wakame2010–2013Dried product as sold | sample value. | ||
| Wakame · driedAlmela et al. 2002 | retail product 10Collection date unreported | sample value. | ||
| Wakame · driedAlmela et al. 2002 | retail product 11Collection date unreported | sample value. | ||
| Wakame · driedAlmela et al. 2002 | retail product 12Collection date unreported | sample value. | ||
| Wakame · driedBralatei et al. 2017 | WakameCollection date unreportedBasis not stated | range. | ||
| Wakame · driedGarcía-Salgado et al. 2012 | Wakame, JapanCollection date unreported | sample value. | ||
| Wakame · driedGarcía-Salgado et al. 2012 | Wakame, SpainCollection date unreported | sample value. | ||
| Wakame · driedLlorente-Mirandes et al. 2011 | Undaria pinnatifidaCollection date unreported | sample value. | ||
| Wakame · driedMatsumoto-Tanibuchi et al. 2019 | Dried wakameCollection date unreportedDried product as sold | below LOD. | ||
| Wakame · driedMcSheehy et al. 2000 | sample KCollection date unreportedDried product as sold | sample value. | ||
| Wakame · driedRose et al. 2007 | Wakame2003Dried product as sold | below LOD. | ||
| Wakame · driedRose et al. 2007 | Wakame2003Dried product as sold | below LOD. | ||
| Wakame · driedRose et al. 2007 | Wakame2003Dried product as sold | below LOD. | ||
| Wakame · driedRose et al. 2007 | Wakame2003Dried product as sold | below LOD. | ||
| Wakame · driedRose et al. 2007 | Wakame2003Dried product as sold | below LOD. | ||
| Arame · driedDuinker et al. 2020 | Eisenia bicyclis2014–2019 | sample value. | ||
| Arame · driedAlmela et al. 2002 | retail product 7Collection date unreported | sample value. | ||
| Arame · driedAlmela et al. 2002 | retail product 8Collection date unreported | sample value. | ||
| Arame · driedAlmela et al. 2002 | retail product 9Collection date unreported | sample value. | ||
| Arame · driedGarcía-Salgado et al. 2012 | Arame, JapanCollection date unreported | sample value. | ||
| Arame · driedRose et al. 2007 | Arame2003Dried product as sold | below LOD. | ||
| Arame · driedRose et al. 2007 | Arame2003Dried product as sold | below LOD. | ||
| Arame · driedRose et al. 2007 | Arame2003Dried product as sold | below LOD. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region EURO; random sampling2013–2023Dried product as sold | median. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region EURO; targeted sampling2022Dried product as sold | median. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region WPRO; random sampling2015–2024Dried product as sold | median. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region WPRO; targeted sampling2010Dried product as sold | median. | ||
| Nori/laver · driedDuinker et al. 2020 | Porphyra spp2014–2019 | mean.Same samples: 10–300 µg/kg (range) | ||
| Nori/laver · driedDuinker et al. 2020 | Porphyra spp2014–2019 | median. | ||
| Nori/laver · driedDuinker et al. 2020 | Porphyra spp2014–2019 | range. | ||
| Nori/laver · driedEFSA 2023 seaweed report | Laver / Dried product2011–2022Dried product as sold | mean. | ||
| Nori/laver · driedEFSA 2023 seaweed report | Laver / Dried product2011–2022Dried product as sold | mean. | ||
| Nori/laver · driedEFSA et al. 2021 | Laver2013–2018Basis not stated | mean. | ||
| Nori/laver · driedEFSA et al. 2021 | Laver2013–2018Basis not stated | mean. | ||
| Nori/laver · driedEFSA et al. 2021 | Laver2013–2018Basis not stated | mean. | ||
| Nori/laver · driedFSANZ 2010 seaweed survey | Nori2010–2013Dried product as sold | mean. | ||
| Nori/laver · driedFSANZ 2010 seaweed survey | Nori2010–2013Dried product as sold | sample value. | ||
| Nori/laver · driedFSANZ 2010 seaweed survey | Nori2010–2013Dried product as sold | sample value. | ||
| Nori/laver · driedFSANZ 2010 seaweed survey | Nori2010–2013Dried product as sold | sample value. | ||
| Nori/laver · driedFSANZ 2010 seaweed survey | Nori2010–2013Dried product as sold | sample value. | ||
| Nori/laver · driedAlmela et al. 2002 | retail product 3Collection date unreported | sample value. | ||
| Nori/laver · driedAlmela et al. 2002 | retail product 4Collection date unreported | sample value. | ||
| Nori/laver · driedBralatei et al. 2017 | NoriCollection date unreportedBasis not stated | range. | ||
| Nori/laver · driedDíaz et al. 2012 | Porphyra columbina2003–2004 | mean. | ||
| Nori/laver · driedGarcía-Salgado et al. 2012 | Nori, JapanCollection date unreported | not detected. | ||
| Nori/laver · driedGarcía-Salgado et al. 2012 | Nori, SpainCollection date unreported | not detected. | ||
| Nori/laver · driedLaparra et al. 2003 | Porphyra sp. rawCollection date unreported | sample value. | ||
| Nori/laver · driedLlorente-Mirandes et al. 2011 | Porphyra purpureaCollection date unreported | below LOD. | ||
| Nori/laver · driedMatsumoto-Tanibuchi et al. 2019 | Dried noriCollection date unreportedDried product as sold | mean. | ||
| Nori/laver · driedMcSheehy et al. 2000 | sample HCollection date unreportedDried product as sold | sample value. | ||
| Nori/laver · driedRose et al. 2007 | Nori2003Dried product as sold | below LOD. | ||
| Nori/laver · driedRose et al. 2007 | Nori2003Dried product as sold | below LOD. | ||
| Nori/laver · driedRose et al. 2007 | Nori2003Dried product as sold | below LOD. | ||
| Nori/laver · driedRose et al. 2007 | Nori2003Dried product as sold | below LOD. | ||
| Nori/laver · driedRose et al. 2007 | Nori2003Dried product as sold | below LOD. | ||
| Nori/laver · driedRose et al. 2007 | Nori2003Dried product as sold | below LOD. | ||
| Nori/laver · driedRose et al. 2007 | Nori2003Dried product as sold | below LOD. | ||
| Nori/laver · driedSim et al. 2024 | P. dioica2020–2022 | mean. | ||
| Nori/laver · driedTaylor et al. 2016 | Porphyra umbilicalus2012Basis not stated | sample value. | ||
| Nori/laver · driedWei et al. 2003 | Porphyra, Dalian producing area2001 | not detected. | ||
| Nori/laver · driedWei et al. 2003 | Porphyra, Fujian producing area2001 | not detected. | ||
| Nori/laver · driedWei et al. 2003 | Porphyra, Guangzhou producing area2001 | not detected. | ||
| Nori/laver · driedWei et al. 2003 | Porphyra, Qingdao producing area2001 | not detected. | ||
| Nori/laver · driedWei et al. 2003 | Porphyra, Zhejiang producing area2001 | not detected. | ||
| Dulse · driedWHO GEMS/Food | WHO region EURO; random sampling2018–2023Dried product as sold | median. | ||
| Dulse · driedWHO GEMS/Food | WHO region EURO; targeted sampling2018–2021Dried product as sold | median. | ||
| Dulse · driedEFSA 2023 seaweed report | Dulse / Dried product2011–2022Dried product as sold | mean. | ||
| Dulse · driedEFSA 2023 seaweed report | Dulse / Dried product2011–2022Dried product as sold | mean. | ||
| Dulse · driedAlmela et al. 2002 | retail product 6Collection date unreported | sample value. | ||
| Dulse · driedMcSheehy et al. 2000 | sample GCollection date unreportedDried product as sold | sample value. | ||
| Dulse · driedSim et al. 2024 | P. palmata2020–2022 | mean. | ||
| Dulse · driedTaylor et al. 2016 | Palmaria palmata2012Basis not stated | mean. | ||
| Sea spaghetti · driedEFSA 2023 seaweed report | Sea spaghetti / Dried product2011–2022Dried product as sold | mean. | ||
| Sea spaghetti · driedEFSA 2023 seaweed report | Sea spaghetti / Dried product2011–2022Dried product as sold | mean. | ||
| Sea spaghetti · driedGarcía-Salgado et al. 2012 | Sea spaghetti, SpainCollection date unreported | sample value. | ||
| Sea spaghetti · driedMcSheehy et al. 2000 | sample DCollection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · driedWHO GEMS/Food | WHO region EURO; random sampling2018–2019Dried product as sold | median. | ||
| Wracks (Fucus/Ascophyllum) · driedEFSA 2023 seaweed report | Rockweed / Dried product2011–2022Dried product as sold | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedEFSA 2023 seaweed report | Rockweed / Dried product2011–2022Dried product as sold | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedAlmela et al. 2002 | retail product 15Collection date unreported | sample value. | ||
| Wracks (Fucus/Ascophyllum) · driedGarcía-Salgado et al. 2012 | Fucus, FranceCollection date unreported | sample value. | ||
| Wracks (Fucus/Ascophyllum) · driedOwnsworth et al. 2019 | Fucus vesiculosusCollection date unreported | range. | ||
| Wracks (Fucus/Ascophyllum) · driedRonan et al. 2017 | Ascophyllum nodosum2015 | range. | ||
| Wracks (Fucus/Ascophyllum) · driedRonan et al. 2017 | Ascophyllum nodosum2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · driedRonan et al. 2017 | Ascophyllum nodosum2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | A. nodosum2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | A. nodosum2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | A. nodosum primary shoot2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | A. nodosum primary shoot2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | F. vesiculosus2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | F. vesiculosus2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Ascophyllum nodosum2012Basis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Ascophyllum nodosum2012Basis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Fucus spiralis2012Basis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Fucus vesiculosus2012Basis not stated | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Fucus vesiculosus2012Basis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedUnknown 2018 | sample 17Collection date unreportedBasis not stated | sample value. | ||
| Carrageen (Irish moss) · driedWHO GEMS/Food | WHO region EURO; random sampling2014–2017Dried product as sold | median. | ||
| Carrageen (Irish moss) · driedWHO GEMS/Food | WHO region EURO; targeted sampling2018Dried product as sold | median. | ||
| Carrageen (Irish moss) · driedEFSA 2023 seaweed report | Carrageen mosses / Dried product2011–2022Dried product as sold | mean. | ||
| Carrageen (Irish moss) · driedEFSA 2023 seaweed report | Carrageen mosses / Dried product2011–2022Dried product as sold | mean. | ||
| Carrageen (Irish moss) · driedLlorente-Mirandes et al. 2011 | Chondrus crispusCollection date unreported | sample value. | ||
| Carrageen (Irish moss) · driedTaylor et al. 2016 | Chondrus crispus2012Basis not stated | sample value. | ||
| Carrageen (Irish moss) · driedTaylor et al. 2016 | Chondrus crispus2012Basis not stated | mean. | ||
| Green seaweeds (Ulva etc.) · driedWHO GEMS/Food | WHO region EURO; random sampling2018–2019Dried product as sold | median. | ||
| Green seaweeds (Ulva etc.) · driedWHO GEMS/Food | WHO region WPRO; random sampling2015–2016Dried product as sold | median. | ||
| Green seaweeds (Ulva etc.) · driedDuinker et al. 2020 | Ulva spp2014–2019 | sample value. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Green algae2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Green algae2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Sea lettuce / Dried product2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Sea lettuce / Dried product2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedAlmela et al. 2002 | retail product 1Collection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · driedAlmela et al. 2002 | retail product 2Collection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · driedDíaz et al. 2012 | Chlorophyceae2003–2004 | mean. | ||
| Green seaweeds (Ulva etc.) · driedDíaz et al. 2012 | Ulva rigida2003–2004 | mean. | ||
| Green seaweeds (Ulva etc.) · driedLaparra et al. 2003 | Enteromorpha sp. rawCollection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · driedLlorente-Mirandes et al. 2011 | Ulva rigidaCollection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · driedMatsumoto-Tanibuchi et al. 2019 | Dried green laverCollection date unreportedDried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedMatsumoto-Tanibuchi et al. 2019 | Dried sea lettuceCollection date unreportedDried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedTaylor et al. 2016 | Chaetomorpha picquotiana2012Basis not stated | sample value. | ||
| Green seaweeds (Ulva etc.) · driedTaylor et al. 2016 | Gayralia oxysperma2012Basis not stated | sample value. | ||
| Green seaweeds (Ulva etc.) · driedTaylor et al. 2016 | Ulva lactuca2012Basis not stated | sample value. | ||
| Green seaweeds (Ulva etc.) · driedTaylor et al. 2016 | Ulva lactuca2012Basis not stated | sample value. | ||
| Green seaweeds (Ulva etc.) · driedTaylor et al. 2016 | Ulva prolifera2012Basis not stated | sample value. | ||
| Other brown · driedWHO GEMS/Food | WHO region EURO; random sampling2018–2023Dried product as sold | median. | ||
| Other brown · driedEFSA 2023 seaweed report | Brown algae2011–2022Dried product as sold | mean. | ||
| Other brown · driedEFSA 2023 seaweed report | Brown algae2011–2022Dried product as sold | mean. | ||
| Other brown · driedDíaz et al. 2012 | Durvillaea antarctica2003–2004 | mean. | ||
| Other brown · driedDíaz et al. 2012 | Phaeophyceae2003–2004 | mean. | ||
| Other brown · driedMatsumoto-Tanibuchi et al. 2019 | Dried mozukuCollection date unreportedDried product as sold | mean. | ||
| Other brown · driedMcSheehy et al. 2000 | sample ACollection date unreportedDried product as sold | sample value. | ||
| Other brown · driedOrtega-Flores et al. 2023 | all samples2018–2019 | range. | ||
| Other brown · driedOrtega-Flores et al. 2023 | rainy season), all morphotypes2018–2019 | mean.Same samples: 11,900–69,300 µg/kg (range) | ||
| Other brown · driedOrtega-Flores et al. 2023 | rainy season), all morphotypes2018–2019 | range. | ||
| Other brown · driedOrtega-Flores et al. 2023 | Sargassum fluitans III annual2018–2019 | mean.Same samples: 20,600–71,500 µg/kg (range) | ||
| Other brown · driedOrtega-Flores et al. 2023 | Sargassum fluitans III annual2018–2019 | range. | ||
| Other brown · driedOrtega-Flores et al. 2023 | Sargassum natans I annual2018–2019 | mean.Same samples: 11,900–47,700 µg/kg (range) | ||
| Other brown · driedOrtega-Flores et al. 2023 | Sargassum natans I annual2018–2019 | range. | ||
| Other brown · driedOrtega-Flores et al. 2023 | Sargassum natans VIII annual2018–2019 | mean.Same samples: 12,600–64,700 µg/kg (range) | ||
| Other brown · driedOrtega-Flores et al. 2023 | Sargassum natans VIII annual2018–2019 | range. | ||
| Other brown · driedOrtega-Flores et al. 2023 | warm-dry season), all morphotypes2018–2019 | mean.Same samples: 22,000–71,500 µg/kg (range) | ||
| Other brown · driedOrtega-Flores et al. 2023 | warm-dry season), all morphotypes2018–2019 | range. | ||
| Other brown · driedOrtega-Flores et al. 2023 | winter season), all morphotypes2018–2019 | mean.Same samples: 15,500–54,200 µg/kg (range) | ||
| Other brown · driedOrtega-Flores et al. 2023 | winter season), all morphotypes2018–2019 | range. | ||
| Other brown · driedTaylor et al. 2016 | Colpomenia marina2012Basis not stated | sample value. | ||
| Other red · driedWHO GEMS/Food | WHO region WPRO; random sampling2015–2024Dried product as sold | median. | ||
| Other red · driedEFSA 2023 seaweed report | Red alga2011–2022Dried product as sold | mean. | ||
| Other red · driedEFSA 2023 seaweed report | Red alga2011–2022Dried product as sold | mean. | ||
| Other red · driedDíaz et al. 2012 | Callophyllis variegata2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Chondracanthus chamissoi2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Gigartina skottsbergii2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Gracilaria chilensis2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Gymnogongrus disciplinalis2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Iridaea laminarioides2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Iridaea spp.2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Mastocarpus papillatus2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Mazzaella laminaroides2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Rhodophyceae2003–2004 | mean. | ||
| Other red · driedSim et al. 2024 | A. taxiformis2020–2022 | mean. | ||
| Other red · driedSim et al. 2024 | C. purpureum2020–2022 | mean. | ||
| Other red · driedTaylor et al. 2016 | Gracliaria vermiculophylla2012Basis not stated | sample value. | ||
| Other red · driedTaylor et al. 2016 | Heterosiphonia japonica2012Basis not stated | sample value. | ||
| Other red · driedTaylor et al. 2016 | Phyllophora pseudoceranoides2012Basis not stated | sample value. | ||
| Other red · driedTaylor et al. 2016 | Polyiphonia lanosa2012Basis not stated | sample value. | ||
| Mixed or unspecified · driedWHO GEMS/Food | WHO region WPRO; random sampling2015–2024Dried product as sold | median. | ||
| Mixed or unspecified · driedWHO GEMS/Food | WHO region WPRO; targeted sampling2010Dried product as sold | median. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | pooled dried algae types2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | pooled dried algae types2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA et al. 2021 | Sea weeds2013–2018Basis not stated | mean. | ||
| Mixed or unspecified · driedEFSA et al. 2021 | Sea weeds2013–2018Basis not stated | mean. | ||
| Mixed or unspecified · driedFSANZ 2010 seaweed survey | Overall2010–2013Dried product as sold | mean.Same samples: 7,800 µg/kg (maximum) | ||
| Mixed or unspecified · driedFSANZ 2010 seaweed survey | Overall2010–2013Dried product as sold | median. | ||
| Mixed or unspecified · driedFSANZ 2010 seaweed survey | Overall2010–2013Dried product as sold | below LOD. | ||
| Mixed or unspecified · driedFSANZ 2010 seaweed survey | Overall2010–2013Dried product as sold | max. | ||
| Mixed or unspecified · driedFSANZ 2010 seaweed survey | Sea vegetable2010–2013Dried product as sold | sample value. | ||
| Mixed or unspecified · driedFSANZ 2010 seaweed survey | Seaweed, type not specified2010–2013Dried product as sold | mean. | ||
| Mixed or unspecified · driedFSANZ 2010 seaweed survey | Seaweed, type not specified2010–2013Dried product as sold | sample value. | ||
| Mixed or unspecified · driedFSANZ 2010 seaweed survey | Seaweed, type not specified2010–2013Dried product as sold | below LOD. | ||
| Mixed or unspecified · driedAlmela et al. 2002 | all 18 productsCollection date unreported | range. | ||
| Mixed or unspecified · driedBralatei et al. 2017 | Kombu, nori and wakameCollection date unreportedBasis not stated | range. | ||
| Mixed or unspecified · driedDíaz et al. 2012 | All 14 species2003–2004 | range. | ||
| Mixed or unspecified · driedMcSheehy et al. 2000 | sample JCollection date unreportedDried product as sold | sample value. | ||
| Mixed or unspecified · driedOwnsworth et al. 2019 | all macroalgae speciatedCollection date unreported | range. | ||
| Mixed or unspecified · driedRose et al. 2007 | Non-hijiki varieties2003Dried product as sold | below LOD. | ||
| Mixed or unspecified · driedTaylor et al. 2016 | Mixed seaweed product "soup1"2012Basis not stated | sample value. | ||
| Mixed or unspecified · driedTaylor et al. 2016 | Mixed seaweed product "soup2"2012Basis not stated | sample value. | ||
3 findings · 1 study | ||||
| Hijiki · powder or flakesWHO GEMS/Food | WHO region WPRO; targeted sampling2014 | median. | ||
| Kombu/kelp · powder or flakesWHO GEMS/Food | WHO region WPRO; random sampling2015–2024Dried product as sold | median. | ||
| Mixed or unspecified · powder or flakesWHO GEMS/Food | WHO region WPRO; random sampling2015–2016Dried product as sold | median. | ||
31 findings · 3 studies | ||||
| Hijiki · form not statedEuropean 2014 | Hijiki2003–2012Basis not stated | mean. | ||
| Hijiki · form not statedEuropean 2014 | Hijiki2003–2012Basis not stated | min. | ||
| Hijiki · form not statedEuropean 2014 | Hijiki2003–2012Basis not stated | max. | ||
| Kombu/kelp · form not statedEuropean 2014 | Kombu2003–2012Basis not stated | mean. | ||
| Kombu/kelp · form not statedEuropean 2014 | Kombu2003–2012Basis not stated | mean. | ||
| Kombu/kelp · form not statedEuropean 2014 | Kombu2003–2012Basis not stated | mean. | ||
| Wakame · form not statedEuropean 2014 | Wakame2003–2012Basis not stated | mean. | ||
| Wakame · form not statedEuropean 2014 | Wakame2003–2012Basis not stated | mean. | ||
| Wakame · form not statedEuropean 2014 | Wakame2003–2012Basis not stated | mean. | ||
| Nori/laver · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Nori/laver · form not statedEuropean 2014 | Laver2003–2012Basis not stated | mean. | ||
| Nori/laver · form not statedEuropean 2014 | Laver2003–2012Basis not stated | mean. | ||
| Nori/laver · form not statedEuropean 2014 | Laver2003–2012Basis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · form not statedWHO GEMS/Food | WHO region EURO; random sampling2017–2019As sold, moisture not stated | median. | ||
| Carrageen (Irish moss) · form not statedWHO GEMS/Food | WHO region EURO; random sampling2014–2023As sold, moisture not stated | median. | ||
| Carrageen (Irish moss) · form not statedWHO GEMS/Food | WHO region EURO; targeted sampling2019–2022As sold, moisture not stated | median. | ||
| Carrageen (Irish moss) · form not statedEuropean 2014 | Irish moss2003–2012Basis not stated | mean. | ||
| Carrageen (Irish moss) · form not statedEuropean 2014 | Irish moss2003–2012Basis not stated | mean. | ||
| Carrageen (Irish moss) · form not statedEuropean 2014 | Irish moss2003–2012Basis not stated | mean. | ||
| Green seaweeds (Ulva etc.) · form not statedWHO GEMS/Food | WHO region EURO; random sampling2017–2021As sold, moisture not stated | median. | ||
| Green seaweeds (Ulva etc.) · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Other brown · form not statedWHO GEMS/Food | WHO region EURO; random sampling2019–2022As sold, moisture not stated | median. | ||
| Other brown · form not statedWHO GEMS/Food | WHO region PAHO; random sampling2014–2021As sold, moisture not stated | median. | ||
| Other brown · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Other brown · form not statedCao et al. 2014 | S. pallidum, Yantai, ShandongCollection date unreportedBasis not stated | sample value. | ||
| Mixed or unspecified · form not statedWHO GEMS/Food | WHO region PAHO; random sampling2015–2021As sold, moisture not stated | median. | ||
| Mixed or unspecified · form not statedWHO GEMS/Food | WHO region PAHO; random sampling2011–2013 | median. | ||
| Mixed or unspecified · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2015–2024As sold, moisture not stated | median. | ||
| Mixed or unspecified · form not statedEuropean 2014 | Sea weed2003–2012Basis not stated | mean. | ||
| Mixed or unspecified · form not statedEuropean 2014 | Sea weed2003–2012Basis not stated | mean. | ||
| Mixed or unspecified · form not statedEuropean 2014 | Sea weed2003–2012Basis not stated | mean. | ||
76 findings · 5 studies · 21 spread figures folded in | ||||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Korean variety, Feb 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Korean variety, Jan 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Korean variety, Mar 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Native variety, Apr 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Native variety, Feb 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Native variety, Jan 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Native variety, Mar 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Native variety, May 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedShimoda et al. 2010 | sample 8; Amatsu; not applicable)Collection date unreported | sample value. | ||
| Hijiki · fresh or wild-collectedShimoda et al. 2010 | sample 9Collection date unreported | sample value. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria digitata2014–2019 | mean.Same samples: 60–79,000 µg/kg (range) | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria digitata2014–2019 | median. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria digitata2014–2019 | range. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria hyperborea2014–2019 | mean.Same samples: 30–41 µg/kg (range) | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria hyperborea2014–2019 | median. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria hyperborea2014–2019 | range. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Saccharina latissima2014–2019 | mean.Same samples: 30–670 µg/kg (range) | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Saccharina latissima2014–2019 | median. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Saccharina latissima2014–2019 | range. | ||
| Kombu/kelp · fresh or wild-collectedEFSA 2023 seaweed report | Kombu / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Kombu/kelp · fresh or wild-collectedEFSA 2023 seaweed report | Kombu / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wakame · fresh or wild-collectedEFSA 2023 seaweed report | Wakame / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wakame · fresh or wild-collectedEFSA 2023 seaweed report | Wakame / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra purpurea2014–2019 | mean.Same samples: 30–190 µg/kg (range) | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra purpurea2014–2019 | median. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra purpurea2014–2019 | range. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra umbilicalis2014–2019 | mean.Same samples: 10–60 µg/kg (range) | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra umbilicalis2014–2019 | median. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra umbilicalis2014–2019 | range. | ||
| Nori/laver · fresh or wild-collectedEFSA 2023 seaweed report | Laver / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Nori/laver · fresh or wild-collectedEFSA 2023 seaweed report | Laver / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Dulse · fresh or wild-collectedDuinker et al. 2020 | Palmaria palmata2014–2019 | mean.Same samples: 20–1,030 µg/kg (range) | ||
| Dulse · fresh or wild-collectedDuinker et al. 2020 | Palmaria palmata2014–2019 | median. | ||
| Dulse · fresh or wild-collectedDuinker et al. 2020 | Palmaria palmata2014–2019 | range. | ||
| Sea spaghetti · fresh or wild-collectedDuinker et al. 2020 | Himanthalia elongata2014–2019 | mean.Same samples: 10–50 µg/kg (range) | ||
| Sea spaghetti · fresh or wild-collectedDuinker et al. 2020 | Himanthalia elongata2014–2019 | median. | ||
| Sea spaghetti · fresh or wild-collectedDuinker et al. 2020 | Himanthalia elongata2014–2019 | range. | ||
| Sea spaghetti · fresh or wild-collectedEFSA 2023 seaweed report | Sea spaghetti / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Sea spaghetti · fresh or wild-collectedEFSA 2023 seaweed report | Sea spaghetti / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Ascophyllum nodosum2014–2019 | mean.Same samples: up to 1,210 µg/kg (range maximum) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Ascophyllum nodosum2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Ascophyllum nodosum2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus serratus2014–2019 | mean.Same samples: 10–560 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus serratus2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus serratus2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus spiralis2014–2019 | mean.Same samples: 30–50 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus spiralis2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus spiralis2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus vesiculosus2014–2019 | mean.Same samples: 20–1,640 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus vesiculosus2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus vesiculosus2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Pelvetia canaliculata2014–2019 | mean.Same samples: 90–120 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Pelvetia canaliculata2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Pelvetia canaliculata2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedEFSA 2023 seaweed report | Rockweed / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedEFSA 2023 seaweed report | Rockweed / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Carrageen (Irish moss) · fresh or wild-collectedDuinker et al. 2020 | Chondrus crispus2014–2019 | mean.Same samples: 210–250 µg/kg (range) | ||
| Carrageen (Irish moss) · fresh or wild-collectedDuinker et al. 2020 | Chondrus crispus2014–2019 | median. | ||
| Carrageen (Irish moss) · fresh or wild-collectedDuinker et al. 2020 | Chondrus crispus2014–2019 | range. | ||
| Carrageen (Irish moss) · fresh or wild-collectedEFSA 2023 seaweed report | Carrageen mosses / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Carrageen (Irish moss) · fresh or wild-collectedEFSA 2023 seaweed report | Carrageen mosses / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Codium fragile2014–2019 | mean.Same samples: 70–210 µg/kg (range) | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Codium fragile2014–2019 | median. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Codium fragile2014–2019 | range. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva intestinalis2014–2019 | mean.Same samples: 20–440 µg/kg (range) | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva intestinalis2014–2019 | median. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva intestinalis2014–2019 | range. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva lactuca2014–2019 | mean.Same samples: 30–450 µg/kg (range) | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva lactuca2014–2019 | median. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva lactuca2014–2019 | range. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Green algae2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Green algae2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Sea lettuce / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Sea lettuce / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Alaria esculenta2014–2019 | mean.Same samples: 30–2,700 µg/kg (range) | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Alaria esculenta2014–2019 | median. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Alaria esculenta2014–2019 | range. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Chorda filum2014–2019 | mean.Same samples: 30–270 µg/kg (range) | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Chorda filum2014–2019 | median. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Chorda filum2014–2019 | range. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Halidrys siliquosa2014–2019 | mean.Same samples: 2,400–42,000 µg/kg (range) | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Halidrys siliquosa2014–2019 | median. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Halidrys siliquosa2014–2019 | range. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Sargassum muticum2014–2019 | mean.Same samples: 48,000–68,000 µg/kg (range) | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Sargassum muticum2014–2019 | median. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Sargassum muticum2014–2019 | range. | ||
| Other brown · fresh or wild-collectedEFSA 2023 seaweed report | pooled fresh/unprocessed brown2011–2022Wet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedEFSA 2023 seaweed report | pooled fresh/unprocessed brown2011–2022Wet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedEFSA 2023 seaweed report | pooled fresh/unprocessed brown2011–2022Wet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedEFSA 2023 seaweed report | pooled fresh/unprocessed brown2011–2022Wet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedMorita et al. 1990 | Table 2 row Sargassum sp.1987 | range. | ||
| Other red · fresh or wild-collectedDuinker et al. 2020 | Vertebrata lanosa2014–2019 | mean.Same samples: 40–1,040 µg/kg (range) | ||
| Other red · fresh or wild-collectedDuinker et al. 2020 | Vertebrata lanosa2014–2019 | median. | ||
| Other red · fresh or wild-collectedDuinker et al. 2020 | Vertebrata lanosa2014–2019 | range. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Centroceras clavulatum1987 | range. | ||
| Mixed or unspecified · fresh or wild-collectedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Wet (fresh) weight | mean. | ||
| Mixed or unspecified · fresh or wild-collectedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Wet (fresh) weight | mean. | ||
5 findings · 3 studies | ||||
| Hijiki · cookedIchikawa et al. 2010 | cooked hijikiCollection date unreportedAs prepared (soaked or cooked) | sample value. | ||
| Hijiki · cookedLaparra et al. 2003 | Hizikia fusiforme cookedCollection date unreported | sample value. | ||
| Hijiki · cookedMatsumoto-Tanibuchi et al. 2019 | Dried boiled hijikiCollection date unreportedDried product as sold | mean. | ||
| Nori/laver · cookedLaparra et al. 2003 | Porphyra sp. cookedCollection date unreported | sample value. | ||
| Other brown · cookedMatsumoto-Tanibuchi et al. 2019 | Dried boiled akamokuCollection date unreportedDried product as sold | mean. | ||
25 findings · 1 study | ||||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | mean. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Kombu/kelp · soaked or rehydratedRose et al. 2007 | Kombu2003As prepared (soaked or cooked) | below LOD. | ||
| Kombu/kelp · soaked or rehydratedRose et al. 2007 | Kombu2003As prepared (soaked or cooked) | below LOD. | ||
| Kombu/kelp · soaked or rehydratedRose et al. 2007 | Kombu2003As prepared (soaked or cooked) | below LOD. | ||
| Kombu/kelp · soaked or rehydratedRose et al. 2007 | Kombu2003As prepared (soaked or cooked) | below LOD. | ||
| Kombu/kelp · soaked or rehydratedRose et al. 2007 | Kombu2003As prepared (soaked or cooked) | below LOD. | ||
| Kombu/kelp · soaked or rehydratedRose et al. 2007 | Kombu2003As prepared (soaked or cooked) | below LOD. | ||
| Kombu/kelp · soaked or rehydratedRose et al. 2007 | Kombu2003As prepared (soaked or cooked) | below LOD. | ||
| Wakame · soaked or rehydratedRose et al. 2007 | Wakame2003As prepared (soaked or cooked) | below LOD. | ||
| Wakame · soaked or rehydratedRose et al. 2007 | Wakame2003As prepared (soaked or cooked) | below LOD. | ||
| Wakame · soaked or rehydratedRose et al. 2007 | Wakame2003As prepared (soaked or cooked) | below LOD. | ||
| Wakame · soaked or rehydratedRose et al. 2007 | Wakame2003As prepared (soaked or cooked) | below LOD. | ||
| Wakame · soaked or rehydratedRose et al. 2007 | Wakame2003As prepared (soaked or cooked) | below LOD. | ||
| Arame · soaked or rehydratedRose et al. 2007 | Arame2003As prepared (soaked or cooked) | below LOD. | ||
| Arame · soaked or rehydratedRose et al. 2007 | Arame2003As prepared (soaked or cooked) | below LOD. | ||
| Arame · soaked or rehydratedRose et al. 2007 | Arame2003As prepared (soaked or cooked) | below LOD. | ||
5 findings · 3 studies | ||||
| Hijiki · powderSim et al. 2024 | Hijiki CRM NMIJ 7405-b2020–2022 | mean. | ||
| Kombu/kelp · powderLuvonga et al. 2021 | SRM 3232 Kelp PowderCollection date unreportedBasis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · powderLuvonga et al. 2021 | Kelp powderCollection date unreported | not detected. | ||
| Green seaweeds (Ulva etc.) · powderSim et al. 2024 | Ulva lactuca CRM BCR-2792020–2022 | mean. | ||
| Other brown · powderSiregar et al. 2025 | All taxa and thallus sections2021 | range. | ||
9 findings · 1 study | ||||
| Kombu/kelp · freshWHO GEMS/Food | WHO region EURO; random sampling2015–2022Wet product as sold or prepared | median. | ||
| Wakame · freshWHO GEMS/Food | WHO region EURO; random sampling2015–2019Wet product as sold or prepared | median. | ||
| Arame · freshWHO GEMS/Food | WHO region EURO; random sampling2018Wet product as sold or prepared | median. | ||
| Nori/laver · freshWHO GEMS/Food | WHO region EURO; random sampling2019–2022Wet product as sold or prepared | median. | ||
| Wracks (Fucus/Ascophyllum) · freshWHO GEMS/Food | WHO region EURO; random sampling2017–2019Wet product as sold or prepared | median. | ||
| Carrageen (Irish moss) · freshWHO GEMS/Food | WHO region EURO; random sampling2016–2017Wet product as sold or prepared | median. | ||
| Green seaweeds (Ulva etc.) · freshWHO GEMS/Food | WHO region EURO; random sampling2018–2020Wet product as sold or prepared | median. | ||
| Other brown · freshWHO GEMS/Food | WHO region EURO; random sampling2016–2022Wet product as sold or prepared | median. | ||
| Other red · freshWHO GEMS/Food | WHO region EURO; random sampling2018Wet product as sold or prepared | median. | ||
9 findings · 2 studies | ||||
| Kombu/kelp · salted, seasoned or preparedWHO GEMS/Food | WHO region WPRO; random sampling2015–2016Wet product as sold or prepared | median. | ||
| Kombu/kelp · salted, seasoned or preparedUnknown 2018 | sample 16Collection date unreportedBasis not stated | sample value. | ||
| Wakame · salted, seasoned or preparedWHO GEMS/Food | WHO region EURO; random sampling2022Wet product as sold or prepared | median. | ||
| Wakame · salted, seasoned or preparedWHO GEMS/Food | WHO region WPRO; random sampling2015–2016Wet product as sold or prepared | median. | ||
| Nori/laver · salted, seasoned or preparedWHO GEMS/Food | WHO region EURO; random sampling2021Wet product as sold or prepared | median. | ||
| Nori/laver · salted, seasoned or preparedWHO GEMS/Food | WHO region WPRO; random sampling2015–2016Wet product as sold or prepared | median. | ||
| Green seaweeds (Ulva etc.) · salted, seasoned or preparedWHO GEMS/Food | WHO region WPRO; random sampling2015Wet product as sold or prepared | median. | ||
| Other red · salted, seasoned or preparedWHO GEMS/Food | WHO region WPRO; random sampling2016–2024Wet product as sold or prepared | median. | ||
| Mixed or unspecified · salted, seasoned or preparedWHO GEMS/Food | WHO region WPRO; random sampling2015–2024Wet product as sold or prepared | median. | ||
19 findings · 2 studies | ||||
| Kombu/kelp · supplementCheyns et al. 2021 | FS282013–2016Dried product as sold | sample value. | ||
| Kombu/kelp · supplementCheyns et al. 2021 | FS292013–2016Dried product as sold | sample value. | ||
| Kombu/kelp · supplementCheyns et al. 2021 | FS302013–2016Dried product as sold | sample value. | ||
| Kombu/kelp · supplementGarcía et al. 2006 | Laminaria digitata capsulesCollection date unreportedBasis not stated | not detected. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS162013–2016Dried product as sold | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS172013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS182013–2016Dried product as sold | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS192013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS202013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS212013–2016Dried product as sold | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS222013–2016Dried product as sold | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS232013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS242013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS252013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS262013–2016Dried product as sold | below LOD. | ||
| Other red · supplementCheyns et al. 2021 | FS312013–2016Dried product as sold | sample value. | ||
| Other red · supplementCheyns et al. 2021 | FS322013–2016Dried product as sold | sample value. | ||
| Other red · supplementCheyns et al. 2021 | FS332013–2016Dried product as sold | sample value. | ||
| Mixed or unspecified · supplementCheyns et al. 2021 | FS272013–2016Dried product as sold | below LOD. | ||
2 findings · 1 study | ||||
| Wakame · frozenWHO GEMS/Food | WHO region EURO; random sampling2019Wet product as sold or prepared | median. | ||
| Mixed or unspecified · frozenWHO GEMS/Food | WHO region WPRO; random sampling2015–2016Wet product as sold or prepared | median. | ||
8 findings · 1 study | ||||
| Wakame · roasted or seasoned snackWHO GEMS/Food | WHO region WPRO; random sampling2016Dried product as sold | median. | ||
| Nori/laver · roasted or seasoned snackWHO GEMS/Food | WHO region EURO; random sampling2018–2023Dried product as sold | median. | ||
| Nori/laver · roasted or seasoned snackWHO GEMS/Food | WHO region EURO; targeted sampling2022Dried product as sold | median. | ||
| Nori/laver · roasted or seasoned snackWHO GEMS/Food | WHO region WPRO; random sampling2015–2016Dried product as sold | median. | ||
| Wracks (Fucus/Ascophyllum) · roasted or seasoned snackWHO GEMS/Food | WHO region EURO; random sampling2019Dried product as sold | median. | ||
| Green seaweeds (Ulva etc.) · roasted or seasoned snackWHO GEMS/Food | WHO region EURO; random sampling2022Dried product as sold | median. | ||
| Mixed or unspecified · roasted or seasoned snackWHO GEMS/Food | WHO region WPRO; random sampling2015–2024Dried product as sold | median. | ||
| Mixed or unspecified · roasted or seasoned snackWHO GEMS/Food | WHO region WPRO; targeted sampling2010Dried product as sold | median. | ||
1 finding · 1 study | ||||
| Nori/laver · roasted or seasonedAlmela et al. 2002 | retail product 5Collection date unreported | sample value. | ||
510 findings · 41 studies · 4 spread figures folded in | ||||
| Hijiki · driedWHO GEMS/Food | WHO region EURO; random sampling2018–2020Dried product as sold | median. | ||
| Hijiki · driedWHO GEMS/Food | WHO region EURO; targeted sampling2022Dried product as sold | median. | ||
| Hijiki · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Hijiki · driedAlmela et al. 2002 | retail product 16Collection date unreported | sample value. | ||
| Hijiki · driedAlmela et al. 2002 | retail product 17Collection date unreported | sample value. | ||
| Hijiki · driedAlmela et al. 2002 | retail product 18Collection date unreported | sample value. | ||
| Hijiki · driedGarcía et al. 2006 | Hijiki, Spanish marketCollection date unreportedBasis not stated | sample value. | ||
| Hijiki · driedGarcía-Salgado et al. 2012 | Hijiki, JapanCollection date unreported | sample value. | ||
| Hijiki · driedGarcía-Salgado et al. 2012 | Hijiki, Japanese commercial sourceCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | China, cooking experiment sampleCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | China, Long Hijiki, sample ACollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | China, Long Hijiki, sample BCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | China, Sprout Hijiki, sample ACollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | China, Sprout Hijiki, sample BCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | Japan, cooking experiment sampleCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | Japan, Long Hijiki, sample ACollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | Japan, Long Hijiki, sample BCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | Japan, Sprout Hijiki, sample ACollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | Japan, Sprout Hijiki, sample BCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | South KoreaCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | South Korea, Long Hijiki, sample ACollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | South Korea, Long Hijiki, sample BCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | South KoreaCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | South KoreaCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2010 | dried hijikiCollection date unreportedBasis not stated | sample value. | ||
| Hijiki · driedLaparra et al. 2003 | Hizikia fusiforme rawCollection date unreported | sample value. | ||
| Hijiki · driedLorenc et al. 2020 | Sample 2Collection date unreportedBasis not stated | sample value. | ||
| Hijiki · driedMcSheehy et al. 2000 | sample BCollection date unreportedDried product as sold | sample value. | ||
| Hijiki · driedMcSheehy et al. 2000 | sample CCollection date unreportedDried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | mean. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedRose et al. 2007 | Hijiki2003Dried product as sold | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 1; China; unknown)Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 2Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 3Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 4Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 5Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 6Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 7Collection date unreported | sample value. | ||
| Hijiki · driedZhao et al. 2014 | Hizikia fusiformis2012 | sample value. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region EURO; random sampling2011–2023Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region EURO; targeted sampling2014–2022Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region EURO; unknown2008–2013Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region WPRO; targeted sampling2015–2017 | median. | ||
| Kombu/kelp · driedEFSA 2023 seaweed report | Kombu / Dried product2011–2022Dried product as sold | mean. | ||
| Kombu/kelp · driedEFSA 2023 seaweed report | Kombu / Dried product2011–2022Dried product as sold | mean. | ||
| Kombu/kelp · driedAlmela et al. 2002 | retail product 13Collection date unreported | sample value. | ||
| Kombu/kelp · driedAlmela et al. 2002 | retail product 14Collection date unreported | sample value. | ||
| Kombu/kelp · driedDíaz et al. 2012 | Lessonia nigrescens2003–2004 | mean. | ||
| Kombu/kelp · driedDíaz et al. 2012 | Macrocystis piryfera2003–2004 | mean. | ||
| Kombu/kelp · driedGarcía-Salgado et al. 2012 | Kombu, FranceCollection date unreported | sample value. | ||
| Kombu/kelp · driedGarcía-Salgado et al. 2012 | Kombu, JapanCollection date unreported | sample value. | ||
| Kombu/kelp · driedGarcía-Salgado et al. 2012 | Kombu, SpainCollection date unreported | sample value. | ||
| Kombu/kelp · driedGarcía-Salgado et al. 2012 | Laminaria, FranceCollection date unreported | sample value. | ||
| Kombu/kelp · driedHwang et al. 2010 | Kelp, East production coast2007 | mean. | ||
| Kombu/kelp · driedHwang et al. 2010 | Kelp, South production coast2007 | mean. | ||
| Kombu/kelp · driedHwang et al. 2010 | Kelp, subtotal2007 | mean. | ||
| Kombu/kelp · driedLlorente-Mirandes et al. 2011 | Laminaria ochroleucaCollection date unreported | sample value. | ||
| Kombu/kelp · driedLlorente-Mirandes et al. 2011 | Laminaria saccharinaCollection date unreported | sample value. | ||
| Kombu/kelp · driedMatsumoto-Tanibuchi et al. 2019 | Dried kelpCollection date unreportedDried product as sold | mean. | ||
| Kombu/kelp · driedMcSheehy et al. 2000 | sample ECollection date unreportedDried product as sold | sample value. | ||
| Kombu/kelp · driedMcSheehy et al. 2000 | sample FCollection date unreportedDried product as sold | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-1Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-2Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-3Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-4Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | Japanese Laminaria japonicaCollection date unreported | range. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | Laminaria digitata, Forth estuaryCollection date unreported | range. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | RMJKCollection date unreported | sample value. | ||
| Kombu/kelp · driedRaab et al. 2024 | Saccharina latissima2019 | mean. | ||
| Kombu/kelp · driedRonan et al. 2017 | Laminaria digitata blades2015 | range. | ||
| Kombu/kelp · driedRonan et al. 2017 | Laminaria digitata2015 | range. | ||
| Kombu/kelp · driedRonan et al. 2017 | Laminaria digitata2015 | max. | ||
| Kombu/kelp · driedRonan et al. 2017 | Laminaria digitata, distal blade2015 | max. | ||
| Kombu/kelp · driedRonan et al. 2017 | Laminaria digitata, whole thalli2015 | mean. | ||
| Kombu/kelp · driedRose et al. 2007 | Kombu2003Dried product as sold | mean. | ||
| Kombu/kelp · driedRose et al. 2007 | Kombu2003Dried product as sold | sample value. | ||
| Kombu/kelp · driedRose et al. 2007 | Kombu2003Dried product as sold | sample value. | ||
| Kombu/kelp · driedRose et al. 2007 | Kombu2003Dried product as sold | sample value. | ||
| Kombu/kelp · driedRose et al. 2007 | Kombu2003Dried product as sold | sample value. | ||
| Kombu/kelp · driedRose et al. 2007 | Kombu2003Dried product as sold | sample value. | ||
| Kombu/kelp · driedRose et al. 2007 | Kombu2003Dried product as sold | sample value. | ||
| Kombu/kelp · driedRose et al. 2007 | Kombu2003Dried product as sold | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Farmed; base of blade2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Farmed; distal tip2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Wild2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Wild2018–2021 | mean. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample I: White Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample II: White Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample III: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample IV: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample V: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample VI: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedSim et al. 2024 | L. digitata2020–2022 | mean. | ||
| Kombu/kelp · driedSim et al. 2024 | L. digitata2020–2022 | mean. | ||
| Kombu/kelp · driedSim et al. 2024 | S. latissima2020–2022 | mean. | ||
| Kombu/kelp · driedSim et al. 2024 | S. latissima2020–2022 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 12023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 22023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 32023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | WWT2023 | mean. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Agarum clathratum2012Basis not stated | sample value. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Alaria esculenta2012Basis not stated | mean. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Brown algae of order Laminariales2012Basis not stated | range. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Laminaria digitata2012Basis not stated | mean. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Laminaria digitata2012Basis not stated | sample value. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Laminaria longicruris2012Basis not stated | mean. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Saccharina latissima2012Basis not stated | sample value. | ||
| Kombu/kelp · driedUnknown 2018 | sample 14Collection date unreportedBasis not stated | sample value. | ||
| Kombu/kelp · driedUnknown 2018 | sample 15Collection date unreportedBasis not stated | sample value. | ||
| Kombu/kelp · driedVan et al. 2004 | Laminaria ingested by volunteersCollection date unreportedBasis not stated | mean. | ||
| Kombu/kelp · driedZhao et al. 2014 | Laminaria japonica2012 | sample value. | ||
| Wakame · driedWHO GEMS/Food | WHO region EURO; random sampling2010–2023Dried product as sold | median. | ||
| Wakame · driedWHO GEMS/Food | WHO region EURO; targeted sampling2019–2022Dried product as sold | median. | ||
| Wakame · driedWHO GEMS/Food | WHO region EURO; unknown2008–2011Dried product as sold | median. | ||
| Wakame · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Wakame · driedWHO GEMS/Food | WHO region WPRO; targeted sampling2015 | median. | ||
| Wakame · driedEFSA 2023 seaweed report | Wakame / Dried product2011–2022Dried product as sold | mean. | ||
| Wakame · driedEFSA 2023 seaweed report | Wakame / Dried product2011–2022Dried product as sold | mean. | ||
| Wakame · driedAlmela et al. 2002 | retail product 10Collection date unreported | sample value. | ||
| Wakame · driedAlmela et al. 2002 | retail product 11Collection date unreported | sample value. | ||
| Wakame · driedAlmela et al. 2002 | retail product 12Collection date unreported | sample value. | ||
| Wakame · driedGarcía-Salgado et al. 2012 | Wakame, JapanCollection date unreported | sample value. | ||
| Wakame · driedGarcía-Salgado et al. 2012 | Wakame, SpainCollection date unreported | sample value. | ||
| Wakame · driedGarcía-Salgado et al. 2012 | Wakame, Japanese commercial sourceCollection date unreported | sample value. | ||
| Wakame · driedHata et al. 2014 | retail dry wakame productCollection date unreported | mean. | ||
| Wakame · driedLlorente-Mirandes et al. 2011 | Undaria pinnatifidaCollection date unreported | sample value. | ||
| Wakame · driedMatsumoto-Tanibuchi et al. 2019 | Dried wakameCollection date unreportedDried product as sold | mean. | ||
| Wakame · driedMcSheehy et al. 2000 | sample KCollection date unreportedDried product as sold | sample value. | ||
| Wakame · driedRose et al. 2007 | Wakame2003Dried product as sold | mean. | ||
| Wakame · driedRose et al. 2007 | Wakame2003Dried product as sold | sample value. | ||
| Wakame · driedRose et al. 2007 | Wakame2003Dried product as sold | sample value. | ||
| Wakame · driedRose et al. 2007 | Wakame2003Dried product as sold | sample value. | ||
| Wakame · driedRose et al. 2007 | Wakame2003Dried product as sold | sample value. | ||
| Wakame · driedRose et al. 2007 | Wakame2003Dried product as sold | sample value. | ||
| Wakame · driedZhao et al. 2014 | Undaria pinnatifida2012 | sample value. | ||
| Arame · driedAlmela et al. 2002 | retail product 7Collection date unreported | sample value. | ||
| Arame · driedAlmela et al. 2002 | retail product 8Collection date unreported | sample value. | ||
| Arame · driedAlmela et al. 2002 | retail product 9Collection date unreported | sample value. | ||
| Arame · driedGarcía-Salgado et al. 2012 | Arame, JapanCollection date unreported | sample value. | ||
| Arame · driedRose et al. 2007 | Arame2003Dried product as sold | mean. | ||
| Arame · driedRose et al. 2007 | Arame2003Dried product as sold | sample value. | ||
| Arame · driedRose et al. 2007 | Arame2003Dried product as sold | sample value. | ||
| Arame · driedRose et al. 2007 | Arame2003Dried product as sold | sample value. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region EURO; random sampling2011–2023Dried product as sold | median. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region EURO; targeted sampling2015–2021Dried product as sold | median. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region EURO; unknown2008–2019Dried product as sold | median. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Nori/laver · driedEFSA 2023 seaweed report | Laver / Dried product2011–2022Dried product as sold | mean. | ||
| Nori/laver · driedEFSA 2023 seaweed report | Laver / Dried product2011–2022Dried product as sold | mean. | ||
| Nori/laver · driedAlmela et al. 2002 | retail product 3Collection date unreported | sample value. | ||
| Nori/laver · driedAlmela et al. 2002 | retail product 4Collection date unreported | sample value. | ||
| Nori/laver · driedDíaz et al. 2012 | Porphyra columbina2003–2004 | mean. | ||
| Nori/laver · driedGarcía-Salgado et al. 2012 | Nori, JapanCollection date unreported | sample value. | ||
| Nori/laver · driedGarcía-Salgado et al. 2012 | Nori, SpainCollection date unreported | sample value. | ||
| Nori/laver · driedHwang et al. 2010 | Laver, South production coast2007 | mean. | ||
| Nori/laver · driedHwang et al. 2010 | Laver, subtotal2007 | mean. | ||
| Nori/laver · driedHwang et al. 2010 | Laver, West production coast2007 | mean. | ||
| Nori/laver · driedLaparra et al. 2003 | Porphyra sp. rawCollection date unreported | sample value. | ||
| Nori/laver · driedLlorente-Mirandes et al. 2011 | Porphyra purpureaCollection date unreported | sample value. | ||
| Nori/laver · driedLorenc et al. 2020 | Sample 3Collection date unreportedBasis not stated | sample value. | ||
| Nori/laver · driedMatsumoto-Tanibuchi et al. 2019 | Dried noriCollection date unreportedDried product as sold | mean. | ||
| Nori/laver · driedMcSheehy et al. 2000 | sample HCollection date unreportedDried product as sold | sample value. | ||
| Nori/laver · driedRose et al. 2007 | Nori2003Dried product as sold | mean. | ||
| Nori/laver · driedRose et al. 2007 | Nori2003Dried product as sold | sample value. | ||
| Nori/laver · driedRose et al. 2007 | Nori2003Dried product as sold | sample value. | ||
| Nori/laver · driedRose et al. 2007 | Nori2003Dried product as sold | sample value. | ||
| Nori/laver · driedRose et al. 2007 | Nori2003Dried product as sold | sample value. | ||
| Nori/laver · driedRose et al. 2007 | Nori2003Dried product as sold | sample value. | ||
| Nori/laver · driedRose et al. 2007 | Nori2003Dried product as sold | sample value. | ||
| Nori/laver · driedRose et al. 2007 | Nori2003Dried product as sold | sample value. | ||
| Nori/laver · driedSim et al. 2024 | P. dioica2020–2022 | mean. | ||
| Nori/laver · driedTaylor et al. 2016 | Porphyra umbilicalus2012Basis not stated | sample value. | ||
| Nori/laver · driedWei et al. 2003 | Porphyra, all five producing areas2001 | mean. | ||
| Nori/laver · driedWei et al. 2003 | Porphyra, Dalian producing area2001 | mean. | ||
| Nori/laver · driedWei et al. 2003 | Porphyra, Fujian producing area2001 | mean. | ||
| Nori/laver · driedWei et al. 2003 | Porphyra, Guangzhou producing area2001 | mean. | ||
| Nori/laver · driedWei et al. 2003 | Porphyra, Qingdao producing area2001 | mean. | ||
| Nori/laver · driedWei et al. 2003 | Porphyra, Zhejiang producing area2001 | mean. | ||
| Nori/laver · driedZhao et al. 2014 | Porphyra yezoensis2012 | sample value. | ||
| Dulse · driedWHO GEMS/Food | WHO region EURO; random sampling2018–2023Dried product as sold | median. | ||
| Dulse · driedWHO GEMS/Food | WHO region EURO; targeted sampling2019–2022Dried product as sold | median. | ||
| Dulse · driedEFSA 2023 seaweed report | Dulse / Dried product2011–2022Dried product as sold | mean. | ||
| Dulse · driedEFSA 2023 seaweed report | Dulse / Dried product2011–2022Dried product as sold | mean. | ||
| Dulse · driedAlmela et al. 2002 | retail product 6Collection date unreported | sample value. | ||
| Dulse · driedBehnaz et al. 2016 | Palmaria palmata, Fornæs, Denmark2011 | mean. | ||
| Dulse · driedMcSheehy et al. 2000 | sample GCollection date unreportedDried product as sold | sample value. | ||
| Dulse · driedSim et al. 2024 | P. palmata2020–2022 | mean. | ||
| Dulse · driedTaylor et al. 2016 | Palmaria palmata2012Basis not stated | mean. | ||
| Sea spaghetti · driedEFSA 2023 seaweed report | Sea spaghetti / Dried product2011–2022Dried product as sold | mean. | ||
| Sea spaghetti · driedEFSA 2023 seaweed report | Sea spaghetti / Dried product2011–2022Dried product as sold | mean. | ||
| Sea spaghetti · driedGarcía-Salgado et al. 2012 | Sea spaghetti, SpainCollection date unreported | sample value. | ||
| Sea spaghetti · driedMcSheehy et al. 2000 | sample DCollection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · driedWHO GEMS/Food | WHO region EURO; random sampling2017–2018Dried product as sold | median. | ||
| Wracks (Fucus/Ascophyllum) · driedEFSA 2023 seaweed report | Rockweed / Dried product2011–2022Dried product as sold | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedEFSA 2023 seaweed report | Rockweed / Dried product2011–2022Dried product as sold | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedAlmela et al. 2002 | retail product 15Collection date unreported | sample value. | ||
| Wracks (Fucus/Ascophyllum) · driedGarcía-Salgado et al. 2012 | Fucus, FranceCollection date unreported | sample value. | ||
| Wracks (Fucus/Ascophyllum) · driedOwnsworth et al. 2019 | Fucus vesiculosus, Forth estuaryCollection date unreported | range. | ||
| Wracks (Fucus/Ascophyllum) · driedRonan et al. 2017 | Ascophyllum nodosum2015 | max. | ||
| Wracks (Fucus/Ascophyllum) · driedRonan et al. 2017 | Ascophyllum nodosum2015 | range. | ||
| Wracks (Fucus/Ascophyllum) · driedRonan et al. 2017 | Ascophyllum nodosum2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · driedRonan et al. 2017 | Ascophyllum nodosum2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · driedRonan et al. 2017 | Ascophyllum nodosum, whole thalli2015 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | A. nodosum2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | A. nodosum2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | F. vesiculosus2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | F. vesiculosus2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Ascophyllum nodosum2012Basis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Ascophyllum nodosum2012Basis not stated | range. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Ascophyllum nodosum2012Basis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Ascophyllum nodosum2012Basis not stated | range. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Fucus spiralis2012Basis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Fucus vesiculosus2012Basis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Fucus vesiculosus2012Basis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedUnknown 2018 | sample 17Collection date unreportedBasis not stated | sample value. | ||
| Carrageen (Irish moss) · driedWHO GEMS/Food | WHO region EURO; random sampling2014–2017Dried product as sold | median. | ||
| Carrageen (Irish moss) · driedWHO GEMS/Food | WHO region EURO; targeted sampling2019Dried product as sold | median. | ||
| Carrageen (Irish moss) · driedEFSA 2023 seaweed report | Carrageen mosses / Dried product2011–2022Dried product as sold | mean. | ||
| Carrageen (Irish moss) · driedEFSA 2023 seaweed report | Carrageen mosses / Dried product2011–2022Dried product as sold | mean. | ||
| Carrageen (Irish moss) · driedBehnaz et al. 2016 | Chondrus crispus, Fornæs, Denmark2011 | mean. | ||
| Carrageen (Irish moss) · driedLlorente-Mirandes et al. 2011 | Chondrus crispusCollection date unreported | sample value. | ||
| Carrageen (Irish moss) · driedTaylor et al. 2016 | Chondrus crispus2012Basis not stated | sample value. | ||
| Carrageen (Irish moss) · driedTaylor et al. 2016 | Chondrus crispus2012Basis not stated | mean. | ||
| Green seaweeds (Ulva etc.) · driedWHO GEMS/Food | WHO region EURO; random sampling2018–2019Dried product as sold | median. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Green algae2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Green algae2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Sea lettuce / Dried product2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Sea lettuce / Dried product2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedAlmela et al. 2002 | retail product 1Collection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · driedAlmela et al. 2002 | retail product 2Collection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · driedAykut et al. 2018 | Kadın Creek2011–2012 | mean. | ||
| Green seaweeds (Ulva etc.) · driedAykut et al. 2018 | Kadın Creek2011–2012 | range. | ||
| Green seaweeds (Ulva etc.) · driedDíaz et al. 2012 | Chlorophyceae2003–2004 | mean. | ||
| Green seaweeds (Ulva etc.) · driedDíaz et al. 2012 | Ulva rigida2003–2004 | mean. | ||
| Green seaweeds (Ulva etc.) · driedHwang et al. 2010 | Sea lettuce2007 | mean. | ||
| Green seaweeds (Ulva etc.) · driedLaparra et al. 2003 | Enteromorpha sp. rawCollection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · driedLlorente-Mirandes et al. 2011 | Ulva rigidaCollection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · driedMatsumoto-Tanibuchi et al. 2019 | Dried green laverCollection date unreportedDried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedMatsumoto-Tanibuchi et al. 2019 | Dried sea lettuceCollection date unreportedDried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedRakib et al. 2021 | Chlorophyta2018–2019 | mean. | ||
| Green seaweeds (Ulva etc.) · driedRakib et al. 2021 | G10 Ulva compressa2018–2019 | mean. | ||
| Green seaweeds (Ulva etc.) · driedRakib et al. 2021 | G8 Caulerpa racemosa2018–2019 | mean. | ||
| Green seaweeds (Ulva etc.) · driedRakib et al. 2021 | G9 Enteromorpha intestinalis2018–2019 | mean. | ||
| Green seaweeds (Ulva etc.) · driedTaylor et al. 2016 | Chaetomorpha picquotiana2012Basis not stated | sample value. | ||
| Green seaweeds (Ulva etc.) · driedTaylor et al. 2016 | Gayralia oxysperma2012Basis not stated | sample value. | ||
| Green seaweeds (Ulva etc.) · driedTaylor et al. 2016 | Ulva lactuca2012Basis not stated | sample value. | ||
| Green seaweeds (Ulva etc.) · driedTaylor et al. 2016 | Ulva lactuca2012Basis not stated | sample value. | ||
| Green seaweeds (Ulva etc.) · driedTaylor et al. 2016 | Ulva prolifera2012Basis not stated | sample value. | ||
| Green seaweeds (Ulva etc.) · driedZhao et al. 2014 | Enteromorpha prolifera2012 | sample value. | ||
| Other brown · driedWHO GEMS/Food | WHO region EURO; random sampling2018–2023Dried product as sold | median. | ||
| Other brown · driedEFSA 2023 seaweed report | Brown algae2011–2022Dried product as sold | mean. | ||
| Other brown · driedEFSA 2023 seaweed report | Brown algae2011–2022Dried product as sold | mean. | ||
| Other brown · driedCao et al. 2014 | S. pallidum, Yantai, ShandongCollection date unreportedBasis not stated | sample value. | ||
| Other brown · driedDíaz et al. 2012 | Durvillaea antarctica2003–2004 | mean. | ||
| Other brown · driedDíaz et al. 2012 | Phaeophyceae2003–2004 | mean. | ||
| Other brown · driedHwang et al. 2010 | Brown seaweed2007 | mean. | ||
| Other brown · driedHwang et al. 2010 | Brown seaweed2007 | mean. | ||
| Other brown · driedHwang et al. 2010 | Brown seaweed, subtotal2007 | mean. | ||
| Other brown · driedMatsumoto-Tanibuchi et al. 2019 | Dried mozukuCollection date unreportedDried product as sold | mean. | ||
| Other brown · driedMcSheehy et al. 2000 | sample ACollection date unreportedDried product as sold | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | all 12 spatial sites2019–2020 | mean. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | all 23 unique homogenised2019–2020 | mean. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Aug 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Dec 20192019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Feb 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Jan 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Jul 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Jun 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Karikari2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Leigh2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Mahanga2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Māhia2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Mākara Beach2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Mar 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | May 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Motuotau Island2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Motuotau Island2019–2020 | mean. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Moutohora Island2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Nov 20192019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Nov 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Oct 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Sep 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Titahi Bay2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Tolaga Bay2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Waihau Bay2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Wellington Harbour2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Wilson Bay2019–2020 | sample value. | ||
| Other brown · driedOrtega-Flores et al. 2023 | all samples2018–2019 | range. | ||
| Other brown · driedOrtega-Flores et al. 2023 | Mexican Caribbean2018–2019 | range. | ||
| Other brown · driedOrtega-Flores et al. 2023 | Sargassum fluitans III annual2018–2019 | mean. | ||
| Other brown · driedOrtega-Flores et al. 2023 | Sargassum natans I annual2018–2019 | mean. | ||
| Other brown · driedOrtega-Flores et al. 2023 | Sargassum natans VIII annual2018–2019 | mean. | ||
| Other brown · driedPetursdottir 2015 | Ectocarpus EC-Abdn2013 | mean. | ||
| Other brown · driedPetursdottir 2015 | Ectocarpus EC-CB, Cruden Bay, UK2013 | mean. | ||
| Other brown · driedPetursdottir 2015 | Ectocarpus EC-Rvk 12-82013 | mean. | ||
| Other brown · driedPetursdottir 2015 | Ectocarpus EC-Rvk 17-82013 | mean. | ||
| Other brown · driedPetursdottir 2015 | Ectocarpus2013 | range. | ||
| Other brown · driedPetursdottir 2015 | Ectocarpus2013 | range. | ||
| Other brown · driedPetursdottir 2015 | Elachista, Newburgh, UK2013 | mean. | ||
| Other brown · driedPetursdottir 2015 | Elachista, Newburgh, UK2013 | sample value. | ||
| Other brown · driedPetursdottir 2015 | Field-collected Ectocarpus2013 | range. | ||
| Other brown · driedPetursdottir 2015 | Hincksia sp.2013 | mean. | ||
| Other brown · driedPetursdottir 2015 | Pylaiella2013 | sample value. | ||
| Other brown · driedPetursdottir 2015 | Pylaiella, Reykjavik, Iceland2013 | mean. | ||
| Other brown · driedRakib et al. 2021 | B5 Padina tetrastromatica2018–2019 | mean. | ||
| Other brown · driedRakib et al. 2021 | B6 Sargassum oligocystum2018–2019 | mean. | ||
| Other brown · driedRakib et al. 2021 | B7 Padina boryana2018–2019 | mean. | ||
| Other brown · driedRakib et al. 2021 | Phaeophyta2018–2019 | mean. | ||
| Other brown · driedRodríguez-Rodríguez et al. 2026 | Raw Sargassum composite2024Basis not stated | sample value. | ||
| Other brown · driedTaylor et al. 2016 | Colpomenia marina2012Basis not stated | sample value. | ||
| Other red · driedEFSA 2023 seaweed report | Red alga2011–2022Dried product as sold | mean. | ||
| Other red · driedEFSA 2023 seaweed report | Red alga2011–2022Dried product as sold | mean. | ||
| Other red · driedAziz et al. 2021 | G. tenuistipitata var. liuiCollection date unreported | sample value. | ||
| Other red · driedBehnaz et al. 2016 | Ahnfeltia plicata, Fornæs, Denmark2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Delesseria sanguinea2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Dilsea carnosa, Fornæs, Denmark2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Furcellaria lumbricalis2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Gracilaria vermiculophylla2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Odonthalia dentata2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Phycodrys rubens, Fornæs, Denmark2011 | mean. | ||
| Other red · driedDíaz et al. 2012 | Callophyllis variegata2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Chondracanthus chamissoi2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Gigartina skottsbergii2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Gracilaria chilensis2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Gymnogongrus disciplinalis2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Iridaea laminarioides2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Iridaea spp.2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Mastocarpus papillatus2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Mazzaella laminaroides2003–2004 | mean. | ||
| Other red · driedDíaz et al. 2012 | Rhodophyceae2003–2004 | mean. | ||
| Other red · driedKhandaker et al. 2021 | all Malaysian samples2018 | mean. | ||
| Other red · driedKhandaker et al. 2021 | Kota Belud farm2018 | mean.Same samples: 4,300–5,700 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Kota Belud farm2018 | range. | ||
| Other red · driedKhandaker et al. 2021 | Langkawi farm2018 | mean.Same samples: 1,350–2,250 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Langkawi farm2018 | range. | ||
| Other red · driedKhandaker et al. 2021 | Semporna farm2018 | mean.Same samples: 4,700–7,900 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Semporna farm2018 | range. | ||
| Other red · driedRakib et al. 2021 | R1 Hypnea musciformis2018–2019 | mean. | ||
| Other red · driedRakib et al. 2021 | R2 Hypnea pannosa2018–2019 | mean. | ||
| Other red · driedRakib et al. 2021 | R3 Jania rubens2018–2019 | mean. | ||
| Other red · driedRakib et al. 2021 | R4 Gelidium pusillum2018–2019 | mean. | ||
| Other red · driedRakib et al. 2021 | Rhodophyta2018–2019 | mean. | ||
| Other red · driedSim et al. 2024 | A. taxiformis2020–2022 | mean. | ||
| Other red · driedSim et al. 2024 | C. purpureum2020–2022 | mean. | ||
| Other red · driedTaylor et al. 2016 | Gracliaria vermiculophylla2012Basis not stated | sample value. | ||
| Other red · driedTaylor et al. 2016 | Heterosiphonia japonica2012Basis not stated | sample value. | ||
| Other red · driedTaylor et al. 2016 | Phyllophora pseudoceranoides2012Basis not stated | sample value. | ||
| Other red · driedTaylor et al. 2016 | Polyiphonia lanosa2012Basis not stated | sample value. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | pooled dried algae types2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | pooled dried algae types2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedAlmela et al. 2002 | all 18 productsCollection date unreported | range. | ||
| Mixed or unspecified · driedBralatei et al. 2017 | Commercial edible seaweedsCollection date unreportedBasis not stated | range. | ||
| Mixed or unspecified · driedDíaz et al. 2012 | All 14 species2003–2004 | range. | ||
| Mixed or unspecified · driedGarcía-Salgado et al. 2012 | all 12 algaeCollection date unreported | range. | ||
| Mixed or unspecified · driedHwang et al. 2010 | All seaweed, final total2007 | mean. | ||
| Mixed or unspecified · driedMcSheehy et al. 2000 | sample JCollection date unreportedDried product as sold | sample value. | ||
| Mixed or unspecified · driedOwnsworth et al. 2019 | Forth estuary macroalgaeCollection date unreported | mean.Same samples: 8,000–135,000 µg/kg (range) | ||
| Mixed or unspecified · driedOwnsworth et al. 2019 | Forth estuary macroalgaeCollection date unreported | range. | ||
| Mixed or unspecified · driedRakib et al. 2021 | mean of 10 species2018–2019 | mean. | ||
| Mixed or unspecified · driedRose et al. 2007 | All samples2003Dried product as sold | range. | ||
| Mixed or unspecified · driedTaylor et al. 2016 | All macroalgae samples2012Basis not stated | range. | ||
| Mixed or unspecified · driedTaylor et al. 2016 | Mixed seaweed product "soup1"2012Basis not stated | sample value. | ||
| Mixed or unspecified · driedTaylor et al. 2016 | Mixed seaweed product "soup2"2012Basis not stated | sample value. | ||
3 findings · 1 study | ||||
| Hijiki · powder or flakesWHO GEMS/Food | WHO region WPRO; targeted sampling2014 | median. | ||
| Kombu/kelp · powder or flakesWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Wakame · powder or flakesWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
189 findings · 10 studies · 3 spread figures folded in | ||||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Korean variety, Feb 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Korean variety, Jan 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Korean variety, Mar 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Native variety, Apr 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Native variety, Feb 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Native variety, Jan 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Native variety, Mar 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Native variety, May 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | organ: air sac2016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | organ: leaf2016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | organ: rhizoid2016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | organ: stem2016 | mean. | ||
| Hijiki · fresh or wild-collectedKaise et al. 1988 | Hizikia fusiforme1987Basis not stated | sample value. | ||
| Hijiki · fresh or wild-collectedKaise et al. 1988 | Hizikia fusiforme1987Basis not stated | sample value. | ||
| Hijiki · fresh or wild-collectedMorita et al. 1990 | Table 2 purification-study row *51987Basis not stated | sample value. | ||
| Hijiki · fresh or wild-collectedShimoda et al. 2010 | sample 8; Amatsu; not applicable)Collection date unreported | sample value. | ||
| Hijiki · fresh or wild-collectedShimoda et al. 2010 | sample 9Collection date unreported | sample value. | ||
| Kombu/kelp · fresh or wild-collectedEFSA 2023 seaweed report | Kombu / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Kombu/kelp · fresh or wild-collectedEFSA 2023 seaweed report | Kombu / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Kombu/kelp · fresh or wild-collectedKaise et al. 1988 | Laminaria japonica1987Basis not stated | sample value. | ||
| Kombu/kelp · fresh or wild-collectedSund et al. 2026 | Unprocessed2023 | mean. | ||
| Wakame · fresh or wild-collectedEFSA 2023 seaweed report | Wakame / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wakame · fresh or wild-collectedEFSA 2023 seaweed report | Wakame / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wakame · fresh or wild-collectedKaise et al. 1988 | Undaria pinnatifida1987Basis not stated | sample value. | ||
| Wakame · fresh or wild-collectedMorita et al. 1990 | Table 2 purification-study row *41987Wet (fresh) weight | sample value. | ||
| Wakame · fresh or wild-collectedMorita et al. 1990 | Table 2 row Undaria pinnatifida1987 | sample value. | ||
| Nori/laver · fresh or wild-collectedEFSA 2023 seaweed report | Laver / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Nori/laver · fresh or wild-collectedEFSA 2023 seaweed report | Laver / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Nori/laver · fresh or wild-collectedKaise et al. 1988 | Porphyra tenera1987Basis not stated | sample value. | ||
| Sea spaghetti · fresh or wild-collectedEFSA 2023 seaweed report | Sea spaghetti / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Sea spaghetti · fresh or wild-collectedEFSA 2023 seaweed report | Sea spaghetti / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedEFSA 2023 seaweed report | Rockweed / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedEFSA 2023 seaweed report | Rockweed / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | mean.Same samples: 16,400–37,000 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | mean.Same samples: 18,700–19,700 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | sample value. | ||
| Carrageen (Irish moss) · fresh or wild-collectedEFSA 2023 seaweed report | Carrageen mosses / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Carrageen (Irish moss) · fresh or wild-collectedEFSA 2023 seaweed report | Carrageen mosses / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Green algae2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Green algae2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Sea lettuce / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Sea lettuce / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedKaise et al. 1988 | Ulva sp.1987Basis not stated | sample value. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedMorita et al. 1990 | Table 2 purification-study row *11987Wet (fresh) weight | sample value. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedMorita et al. 1990 | Table 2 row Ulva pertusa1987 | sample value. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedMorita et al. 1990 | Table 2 row Ulva arasakii1987 | sample value. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedMorita et al. 1990 | Table 2 row Bryopsis maxima1987 | sample value. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedMorita et al. 1990 | Table 2 row Caulerpa brachypus1987 | sample value. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedMorita et al. 1990 | Table 2 row Codium fragile1987 | sample value. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedSundhar et al. 2023 | C. racemosa RawCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedSundhar et al. 2023 | U. lactuca RawCollection date unreportedWet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedEFSA 2023 seaweed report | pooled fresh/unprocessed brown2011–2022Wet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedEFSA 2023 seaweed report | pooled fresh/unprocessed brown2011–2022Wet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedFattorini et al. 2004 | Dictyota sp., La Milpa2001 | mean. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | mean.Same samples: 56,700–98,900 µg/kg (range) | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | median. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | range. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedKaise et al. 1988 | Ecklonia cava1987Basis not stated | sample value. | ||
| Other brown · fresh or wild-collectedKaise et al. 1988 | Ishige okamurai1987Basis not stated | sample value. | ||
| Other brown · fresh or wild-collectedMorita et al. 1990 | Table 2 purification-study row *21987Wet (fresh) weight | sample value. | ||
| Other brown · fresh or wild-collectedMorita et al. 1990 | Table 2 purification-study row *61987Wet (fresh) weight | sample value. | ||
| Other brown · fresh or wild-collectedMorita et al. 1990 | Table 2 row Spatoglossum pacificum1987 | sample value. | ||
| Other brown · fresh or wild-collectedMorita et al. 1990 | Table 2 row Pachydictyon coriaceum1987 | sample value. | ||
| Other brown · fresh or wild-collectedMorita et al. 1990 | Table 2 row Dictyopteris prolifera1987 | sample value. | ||
| Other brown · fresh or wild-collectedMorita et al. 1990 | Table 2 row Padina arborescens1987 | sample value. | ||
| Other brown · fresh or wild-collectedMorita et al. 1990 | Table 2 row Heterochordaria1987 | sample value. | ||
| Other brown · fresh or wild-collectedMorita et al. 1990 | Table 2 row Myelophycus1987 | sample value. | ||
| Other brown · fresh or wild-collectedMorita et al. 1990 | Table 2 row Sargassum sp.1987 | sample value. | ||
| Other red · fresh or wild-collectedFattorini et al. 2004 | Hypnea spinella, Marina Puerto Sol2001 | mean. | ||
| Other red · fresh or wild-collectedFattorini et al. 2004 | Laurencia papillosa, La Milpa2001 | mean. | ||
| Other red · fresh or wild-collectedKaise et al. 1988 | Chondrus ocellatus1987Basis not stated | sample value. | ||
| Other red · fresh or wild-collectedKaise et al. 1988 | Gelidium amansii1987Basis not stated | sample value. | ||
| Other red · fresh or wild-collectedKaise et al. 1988 | Gloiopeltis tenax1987Basis not stated | sample value. | ||
| Other red · fresh or wild-collectedKaise et al. 1988 | Hypnea charoides1987Basis not stated | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Grateloupia turuturu1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Cyrtymenia sparsa1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Carpopeltis flabellata1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Carpopeltis crispata1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Gloiopeltis furcata1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Schizymenia dubyi1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Hypnea charoides1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Hypnea japonica1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Hypnea variabilis1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Ahnfeltia paradoxa1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Gigartina intermedia1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Chondrus ocellatus1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Chondrus verrucosus1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Chondrus sp.1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Coeloseira pacifica1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Lomentaria catenata1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Psilothallia dentata1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Campylaephora crassa1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Centroceras clavulatum1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Chondria crassicaulis1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Laurencia okamurai1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Gelidium divaricatum1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Corallina pilulifera1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Grateloupia1987 | sample value. | ||
| Other red · fresh or wild-collectedMorita et al. 1990 | Table 2 row Grateloupia okamurai1987 | sample value. | ||
| Other red · fresh or wild-collectedSundhar et al. 2023 | K. aliverzii RawCollection date unreportedWet (fresh) weight | mean. | ||
| Mixed or unspecified · fresh or wild-collectedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Wet (fresh) weight | mean. | ||
| Mixed or unspecified · fresh or wild-collectedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Wet (fresh) weight | mean. | ||
| Mixed or unspecified · fresh or wild-collectedRakib et al. 2021 | mean of 10 species2018–2019Wet (fresh) weight | mean. | ||
21 findings · 7 studies | ||||
| Hijiki · cookedIchikawa et al. 2006 | China, after soaking and cookingCollection date unreported | sample value. | ||
| Hijiki · cookedIchikawa et al. 2006 | Japan, after soaking and cookingCollection date unreported | sample value. | ||
| Hijiki · cookedIchikawa et al. 2006 | South KoreaCollection date unreported | sample value. | ||
| Hijiki · cookedIchikawa et al. 2010 | cooked hijikiCollection date unreportedAs prepared (soaked or cooked) | sample value. | ||
| Hijiki · cookedLaparra et al. 2003 | Hizikia fusiforme cookedCollection date unreported | sample value. | ||
| Hijiki · cookedMatsumoto-Tanibuchi et al. 2019 | Dried boiled hijikiCollection date unreportedDried product as sold | mean. | ||
| Kombu/kelp · cookedVan et al. 2004 | boiled Laminaria after SGFCollection date unreportedBasis not stated | range. | ||
| Kombu/kelp · cookedWang et al. 2020 | Jilin ProvinceCollection date unreportedAs prepared (soaked or cooked) | mean. | ||
| Kombu/kelp · cookedWang et al. 2020 | Other AreaCollection date unreportedAs prepared (soaked or cooked) | mean. | ||
| Kombu/kelp · cookedWang et al. 2020 | Songhua River AreaCollection date unreportedAs prepared (soaked or cooked) | mean. | ||
| Nori/laver · cookedLaparra et al. 2003 | Porphyra sp. cookedCollection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa BoiledCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa MWCCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa SCTCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca BoiledCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca MWCCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca SCTCollection date unreportedWet (fresh) weight | mean. | ||
| Other brown · cookedMatsumoto-Tanibuchi et al. 2019 | Dried boiled akamokuCollection date unreportedDried product as sold | mean. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii BoiledCollection date unreportedWet (fresh) weight | mean. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii MWCCollection date unreportedWet (fresh) weight | mean. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii SCTCollection date unreportedWet (fresh) weight | mean. | ||
84 findings · 12 studies · 3 spread figures folded in | ||||
| Hijiki · powderLorenc et al. 2020 | Sample 1Collection date unreportedBasis not stated | sample value. | ||
| Hijiki · powderNarukawa et al. 2020 | candidate CRM 7405-bCollection date unreported | mean. | ||
| Hijiki · powderNarukawa et al. 2020 | candidate CRM 7405-b, Lab 1Collection date unreported | mean. | ||
| Hijiki · powderNarukawa et al. 2020 | candidate CRM 7405-b, Lab 2Collection date unreported | mean. | ||
| Hijiki · powderNarukawa et al. 2020 | NMIJ CRM 7405-a certified valueCollection date unreported | mean. | ||
| Hijiki · powderNarukawa et al. 2020 | NMIJ CRM 7405-a, Lab 1Collection date unreported | mean. | ||
| Hijiki · powderNarukawa et al. 2020 | NMIJ CRM 7405-a, Lab 2Collection date unreported | mean. | ||
| Hijiki · powderSim et al. 2024 | Hijiki CRM NMIJ 7405-b2020–2022 | mean. | ||
| Kombu/kelp · powderLorenc et al. 2020 | Sample 5Collection date unreportedBasis not stated | sample value. | ||
| Kombu/kelp · powderNischwitz et al. 2006 | KE10Collection date unreportedDried product as sold | sample value. | ||
| Kombu/kelp · powderNischwitz et al. 2006 | KE7Collection date unreportedDried product as sold | sample value. | ||
| Kombu/kelp · powderNischwitz et al. 2006 | KE8Collection date unreportedDried product as sold | sample value. | ||
| Kombu/kelp · powderNischwitz et al. 2006 | KE9Collection date unreportedDried product as sold | sample value. | ||
| Kombu/kelp · powderTukai et al. 2002 | Ecklonia radiata, Sydney NSW2000 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderLorenc et al. 2020 | Sample 4Collection date unreportedBasis not stated | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderLuvonga et al. 2021 | Kelp powderCollection date unreported | mean. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE1Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE11Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE12Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE2Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE3Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE4Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE5Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE6Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderSiregar et al. 2025 | Fucus vesiculosus2021 | mean. | ||
| Wracks (Fucus/Ascophyllum) · powderSiregar et al. 2025 | Fucus vesiculosus2021 | mean. | ||
| Wracks (Fucus/Ascophyllum) · powderSiregar et al. 2025 | Fucus vesiculosus2021 | mean. | ||
| Wracks (Fucus/Ascophyllum) · powderSiregar et al. 2025 | Fucus vesiculosus2021 | mean. | ||
| Wracks (Fucus/Ascophyllum) · powderSiregar et al. 2025 | Fucus vesiculosus2021 | mean. | ||
| Green seaweeds (Ulva etc.) · powderNour et al. 2025 | Ulva clathrata2021 | mean. | ||
| Green seaweeds (Ulva etc.) · powderSim et al. 2024 | Ulva lactuca CRM BCR-2792020–2022 | mean. | ||
| Green seaweeds (Ulva etc.) · powderTukai et al. 2002 | Cladophora subsimplex, Sydney NSW2000 | sample value. | ||
| Green seaweeds (Ulva etc.) · powderTukai et al. 2002 | Codium lucasii, Sydney NSW2000 | sample value. | ||
| Green seaweeds (Ulva etc.) · powderTukai et al. 2002 | Green macroalgae, all sites2000 | mean.Same samples: 120–30,200 µg/kg (range) | ||
| Green seaweeds (Ulva etc.) · powderTukai et al. 2002 | Green macroalgae, all sites2000 | range. | ||
| Green seaweeds (Ulva etc.) · powderTukai et al. 2002 | Ulva lactuta, Sydney NSW2000 | sample value. | ||
| Other brown · powderGarcía et al. 2006 | CRM NIES No. 9Collection date unreportedBasis not stated | sample value. | ||
| Other brown · powderGarcía-Salgado et al. 2012 | CRM NIES No. 9Collection date unreportedBasis not stated | sample value. | ||
| Other brown · powderGarcía-Salgado et al. 2012 | CRM NIES No. 9Collection date unreported | sample value. | ||
| Other brown · powderNour et al. 2025 | Padina pavonica2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Sargassum ilicifolium2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Sargassum latifolium2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Turbinaria decurrens2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystophora monilifera2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystophora monilifera2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystophora monilifera2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystophora monilifera2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystophora monilifera2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystoseira trinodis2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystoseira trinodis2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystoseira trinodis2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystoseira trinodis2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystoseira trinodis2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Hormosira banksia2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Hormosira banksii2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Hormosira banksii2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Hormosira banksii2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Lobospira bicuspidata2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Lobospira bicuspidata2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Lobospira bicuspidata2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Lobospira bicuspidata2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Lobospira bicuspidata2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Pachydictyon paniculatum2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Pachydictyon paniculatum2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Pachydictyon paniculatum2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Pachydictyon paniculatum2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Pachydictyon paniculatum2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Phylospora comosa2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Phylospora comosa2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Phylospora comosa2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Phylospora comosa2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Phylospora comosa2021 | mean. | ||
| Other brown · powderTukai et al. 2002 | Brown macroalgae, all sites2000 | mean.Same samples: 5,000–173,000 µg/kg (range) | ||
| Other brown · powderTukai et al. 2002 | Brown macroalgae, all sites2000 | range. | ||
| Other brown · powderTukai et al. 2002 | Hormosira banksii, Sydney NSW2000 | sample value. | ||
| Other brown · powderTukai et al. 2002 | Lobophora sp., Sydney NSW2000 | sample value. | ||
| Other brown · powderTukai et al. 2002 | Padina fraseri, Sydney NSW2000 | sample value. | ||
| Other brown · powderTukai et al. 2002 | Sargassum sp., Sydney NSW2000 | sample value. | ||
| Other red · powderNour et al. 2025 | Hypnea musciformis2021 | mean. | ||
| Other red · powderTukai et al. 2002 | Amphiroa anceps, Sydney NSW2000 | sample value. | ||
| Other red · powderTukai et al. 2002 | Champia viridis, Sydney NSW2000 | sample value. | ||
| Other red · powderTukai et al. 2002 | Corallina officinalis, Sydney NSW2000 | sample value. | ||
| Other red · powderTukai et al. 2002 | Laurencia sp., Sydney NSW2000 | sample value. | ||
| Other red · powderTukai et al. 2002 | Martensia fragilis, Sydney NSW2000 | sample value. | ||
| Other red · powderTukai et al. 2002 | Red macroalgae, all sites2000 | mean.Same samples: 110–16,900 µg/kg (range) | ||
| Other red · powderTukai et al. 2002 | Red macroalgae, all sites2000 | range. | ||
| Mixed or unspecified · powderEFSA 2009 | Algae as food2003–2008Basis not stated | sample value. | ||
28 findings · 1 study | ||||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | mean. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Hijiki · soaked or rehydratedRose et al. 2007 | Hijiki2003As prepared (soaked or cooked) | sample value. | ||
| Kombu/kelp · soaked or rehydratedRose et al. 2007 | Kombu2003As prepared (soaked or cooked) | mean. | ||
| Kombu/kelp · soaked or rehydratedRose et al. 2007 | Kombu2003As prepared (soaked or cooked) | sample value. | ||
| Kombu/kelp · soaked or rehydratedRose et al. 2007 | Kombu2003As prepared (soaked or cooked) | sample value. | ||
| Kombu/kelp · soaked or rehydratedRose et al. 2007 | Kombu2003As prepared (soaked or cooked) | sample value. | ||
| Kombu/kelp · soaked or rehydratedRose et al. 2007 | Kombu2003As prepared (soaked or cooked) | sample value. | ||
| Kombu/kelp · soaked or rehydratedRose et al. 2007 | Kombu2003As prepared (soaked or cooked) | sample value. | ||
| Kombu/kelp · soaked or rehydratedRose et al. 2007 | Kombu2003As prepared (soaked or cooked) | sample value. | ||
| Kombu/kelp · soaked or rehydratedRose et al. 2007 | Kombu2003As prepared (soaked or cooked) | sample value. | ||
| Wakame · soaked or rehydratedRose et al. 2007 | Wakame2003As prepared (soaked or cooked) | mean. | ||
| Wakame · soaked or rehydratedRose et al. 2007 | Wakame2003As prepared (soaked or cooked) | sample value. | ||
| Wakame · soaked or rehydratedRose et al. 2007 | Wakame2003As prepared (soaked or cooked) | sample value. | ||
| Wakame · soaked or rehydratedRose et al. 2007 | Wakame2003As prepared (soaked or cooked) | sample value. | ||
| Wakame · soaked or rehydratedRose et al. 2007 | Wakame2003As prepared (soaked or cooked) | sample value. | ||
| Wakame · soaked or rehydratedRose et al. 2007 | Wakame2003As prepared (soaked or cooked) | sample value. | ||
| Arame · soaked or rehydratedRose et al. 2007 | Arame2003As prepared (soaked or cooked) | mean. | ||
| Arame · soaked or rehydratedRose et al. 2007 | Arame2003As prepared (soaked or cooked) | sample value. | ||
| Arame · soaked or rehydratedRose et al. 2007 | Arame2003As prepared (soaked or cooked) | sample value. | ||
| Arame · soaked or rehydratedRose et al. 2007 | Arame2003As prepared (soaked or cooked) | sample value. | ||
30 findings · 5 studies | ||||
| Hijiki · form not statedZhao et al. 2025 | control groupCollection date unreported | mean. | ||
| Kombu/kelp · form not statedZhao et al. 2016 | Laminaria japonicaCollection date unreportedWet (fresh) weight | range. | ||
| Nori/laver · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Nori/laver · form not statedZhao et al. 2016 | Porphyra teneraCollection date unreported | range. | ||
| Dulse · form not statedEFSA 2023 seaweed report | Dulse / Unspecified2011–2022Basis not stated | mean. | ||
| Dulse · form not statedEFSA 2023 seaweed report | Dulse / Unspecified2011–2022Basis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · form not statedWHO GEMS/Food | WHO region EURO; random sampling2016–2023As sold, moisture not stated | median. | ||
| Wracks (Fucus/Ascophyllum) · form not statedWHO GEMS/Food | WHO region EURO; targeted sampling2018–2021As sold, moisture not stated | median. | ||
| Carrageen (Irish moss) · form not statedWHO GEMS/Food | WHO region EURO; random sampling2014–2023As sold, moisture not stated | median. | ||
| Carrageen (Irish moss) · form not statedWHO GEMS/Food | WHO region EURO; targeted sampling2014–2022As sold, moisture not stated | median. | ||
| Green seaweeds (Ulva etc.) · form not statedWHO GEMS/Food | WHO region EURO; random sampling2017–2023As sold, moisture not stated | median. | ||
| Green seaweeds (Ulva etc.) · form not statedWHO GEMS/Food | WHO region EURO; random sampling2016 | median. | ||
| Green seaweeds (Ulva etc.) · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Other brown · form not statedWHO GEMS/Food | WHO region EURO; random sampling2018–2023As sold, moisture not stated | median. | ||
| Other brown · form not statedWHO GEMS/Food | WHO region EURO; random sampling2016–2017 | median. | ||
| Other brown · form not statedWHO GEMS/Food | WHO region EURO; targeted sampling2021As sold, moisture not stated | median. | ||
| Other brown · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Other red · form not statedWHO GEMS/Food | WHO region EURO; random sampling2016 | median. | ||
| Other red · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Mixed or unspecified · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Mixed or unspecified · form not statedEFSA 2009 | Algae as food2003–2008Basis not stated | 5th percentile. | ||
| Mixed or unspecified · form not statedEFSA 2009 | Algae as food2003–2008Basis not stated | 5th percentile. | ||
| Mixed or unspecified · form not statedEFSA 2009 | Algae as food2003–2008Basis not stated | 95th percentile. | ||
| Mixed or unspecified · form not statedEFSA 2009 | Algae as food2003–2008Basis not stated | 95th percentile. | ||
| Mixed or unspecified · form not statedEFSA 2009 | Algae as food2003–2008Basis not stated | mean. | ||
| Mixed or unspecified · form not statedEFSA 2009 | Algae as food2003–2008Basis not stated | mean. | ||
| Mixed or unspecified · form not statedEFSA 2009 | Algae as food2003–2008Basis not stated | median. | ||
| Mixed or unspecified · form not statedEFSA 2009 | Algae as food2003–2008Basis not stated | median. | ||
| Mixed or unspecified · form not statedEFSA 2009 | Algae as food2003–2008Basis not stated | max. | ||
| Mixed or unspecified · form not statedEFSA 2009 | Algae as food2003–2008Basis not stated | max. | ||
12 findings · 1 study | ||||
| Kombu/kelp · freshWHO GEMS/Food | WHO region EURO; random sampling2015–2020Wet product as sold or prepared | median. | ||
| Kombu/kelp · freshWHO GEMS/Food | WHO region EURO; targeted sampling2019Wet product as sold or prepared | median. | ||
| Wakame · freshWHO GEMS/Food | WHO region EURO; random sampling2015–2019Wet product as sold or prepared | median. | ||
| Arame · freshWHO GEMS/Food | WHO region EURO; random sampling2018Wet product as sold or prepared | median. | ||
| Nori/laver · freshWHO GEMS/Food | WHO region EURO; random sampling2017–2019Wet product as sold or prepared | median. | ||
| Wracks (Fucus/Ascophyllum) · freshWHO GEMS/Food | WHO region EURO; random sampling2016–2019Wet product as sold or prepared | median. | ||
| Wracks (Fucus/Ascophyllum) · freshWHO GEMS/Food | WHO region EURO; targeted sampling2019Wet product as sold or prepared | median. | ||
| Carrageen (Irish moss) · freshWHO GEMS/Food | WHO region EURO; random sampling2015–2017Wet product as sold or prepared | median. | ||
| Carrageen (Irish moss) · freshWHO GEMS/Food | WHO region EURO; targeted sampling2019Wet product as sold or prepared | median. | ||
| Green seaweeds (Ulva etc.) · freshWHO GEMS/Food | WHO region EURO; random sampling2018–2020Wet product as sold or prepared | median. | ||
| Other brown · freshWHO GEMS/Food | WHO region EURO; random sampling2016–2019Wet product as sold or prepared | median. | ||
| Other red · freshWHO GEMS/Food | WHO region EURO; random sampling2018Wet product as sold or prepared | median. | ||
20 findings · 3 studies | ||||
| Kombu/kelp · supplementCheyns et al. 2021 | FS282013–2016Dried product as sold | sample value. | ||
| Kombu/kelp · supplementCheyns et al. 2021 | FS292013–2016Dried product as sold | sample value. | ||
| Kombu/kelp · supplementCheyns et al. 2021 | FS302013–2016Dried product as sold | sample value. | ||
| Kombu/kelp · supplementGarcía et al. 2006 | Laminaria digitata capsulesCollection date unreportedBasis not stated | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementEFSA 2009 | Algae based supplements2003–2008Basis not stated | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS162013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS172013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS182013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS192013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS202013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS212013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS222013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS232013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS242013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS252013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS262013–2016Dried product as sold | sample value. | ||
| Other red · supplementCheyns et al. 2021 | FS312013–2016Dried product as sold | sample value. | ||
| Other red · supplementCheyns et al. 2021 | FS322013–2016Dried product as sold | sample value. | ||
| Other red · supplementCheyns et al. 2021 | FS332013–2016Dried product as sold | sample value. | ||
| Mixed or unspecified · supplementCheyns et al. 2021 | FS272013–2016Dried product as sold | sample value. | ||
10 findings · 3 studies | ||||
| Kombu/kelp · salted, seasoned or preparedUnknown 2018 | sample 16Collection date unreportedBasis not stated | sample value. | ||
| Wakame · salted, seasoned or preparedWHO GEMS/Food | WHO region EURO; random sampling2022Wet product as sold or prepared | median. | ||
| Wakame · salted, seasoned or preparedWHO GEMS/Food | WHO region WPRO; targeted sampling2015Wet product as sold or prepared | median. | ||
| Nori/laver · salted, seasoned or preparedWHO GEMS/Food | WHO region EURO; random sampling2021Wet product as sold or prepared | median. | ||
| Dulse · salted, seasoned or preparedWHO GEMS/Food | WHO region EURO; random sampling2017Wet product as sold or prepared | median. | ||
| Green seaweeds (Ulva etc.) · salted, seasoned or preparedWHO GEMS/Food | WHO region EURO; random sampling2017Wet product as sold or prepared | median. | ||
| Other brown · salted, seasoned or preparedWHO GEMS/Food | WHO region EURO; random sampling2017Wet product as sold or prepared | median. | ||
| Mixed or unspecified · salted, seasoned or preparedKim et al. 2023 | Sea algae2021Basis not stated | mean. | ||
| Mixed or unspecified · salted, seasoned or preparedKim et al. 2023 | Sea algae2021Basis not stated | min. | ||
| Mixed or unspecified · salted, seasoned or preparedKim et al. 2023 | Sea algae2021Basis not stated | max. | ||
1 finding · 1 study | ||||
| Wakame · frozenWHO GEMS/Food | WHO region EURO; random sampling2019Wet product as sold or prepared | median. | ||
2 findings · 1 study | ||||
| Nori/laver · roasted or seasoned snackWHO GEMS/Food | WHO region EURO; random sampling2017–2023Dried product as sold | median. | ||
| Green seaweeds (Ulva etc.) · roasted or seasoned snackWHO GEMS/Food | WHO region EURO; random sampling2022Dried product as sold | median. | ||
1 finding · 1 study | ||||
| Nori/laver · roasted or seasonedAlmela et al. 2002 | retail product 5Collection date unreported | sample value. | ||
104 findings · 14 studies · 2 spread figures folded in | ||||
| Hijiki · driedGarcía et al. 2006 | Hijiki, Spanish marketCollection date unreportedBasis not stated | not detected. | ||
| Hijiki · driedGarcía-Salgado et al. 2012 | Hijiki, JapanCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | China, Long Hijiki, sample ACollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | China, Long Hijiki, sample BCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | China, Sprout Hijiki, sample ACollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | China, Sprout Hijiki, sample BCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | Japan, Long Hijiki, sample ACollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | Japan, Long Hijiki, sample BCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | Japan, Sprout Hijiki, sample ACollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | Japan, Sprout Hijiki, sample BCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | South Korea, Long Hijiki, sample ACollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | South Korea, Long Hijiki, sample BCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | South KoreaCollection date unreported | sample value. | ||
| Hijiki · driedIchikawa et al. 2006 | South KoreaCollection date unreported | sample value. | ||
| Hijiki · driedLorenc et al. 2020 | Sample 2Collection date unreportedBasis not stated | sample value. | ||
| Hijiki · driedLorenc et al. 2020 | Sample 2Collection date unreportedBasis not stated | below LOD. | ||
| Hijiki · driedLorenc et al. 2020 | Sample 2Collection date unreportedBasis not stated | below LOD. | ||
| Hijiki · driedLorenc et al. 2020 | Sample 2Collection date unreportedBasis not stated | below LOD. | ||
| Hijiki · driedLorenc et al. 2020 | Sample 2aCollection date unreportedBasis not stated | sample value. | ||
| Hijiki · driedLorenc et al. 2020 | Sample 2aCollection date unreportedBasis not stated | sample value. | ||
| Hijiki · driedLorenc et al. 2020 | Sample 2aCollection date unreportedBasis not stated | below LOD. | ||
| Hijiki · driedLorenc et al. 2020 | Sample 2aCollection date unreportedBasis not stated | below LOD. | ||
| Hijiki · driedShimoda et al. 2010 | sample 1; China; unknown)Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 2Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 3Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 4Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 5Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 6Collection date unreported | sample value. | ||
| Hijiki · driedShimoda et al. 2010 | sample 7Collection date unreported | sample value. | ||
| Hijiki · driedZhao et al. 2014 | Hizikia fusiformis water extract2012 | sample value. | ||
| Kombu/kelp · driedGarcía-Salgado et al. 2012 | Kombu, FranceCollection date unreported | sample value. | ||
| Kombu/kelp · driedGarcía-Salgado et al. 2012 | Kombu, JapanCollection date unreported | sample value. | ||
| Kombu/kelp · driedGarcía-Salgado et al. 2012 | Kombu, SpainCollection date unreported | not detected. | ||
| Kombu/kelp · driedGarcía-Salgado et al. 2012 | Laminaria, FranceCollection date unreported | not detected. | ||
| Kombu/kelp · driedLlorente-Mirandes et al. 2011 | Laminaria ochroleucaCollection date unreported | sample value. | ||
| Kombu/kelp · driedLlorente-Mirandes et al. 2011 | Laminaria saccharinaCollection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | Laminaria digitataCollection date unreported | range. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | Laminaria japonicaCollection date unreported | range. | ||
| Kombu/kelp · driedSim et al. 2024 | L. digitata2020–2022 | mean. | ||
| Kombu/kelp · driedSim et al. 2024 | L. digitata2020–2022 | mean. | ||
| Kombu/kelp · driedSim et al. 2024 | S. latissima2020–2022 | mean. | ||
| Kombu/kelp · driedSim et al. 2024 | S. latissima2020–2022 | mean. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Agarum clathratum2012Basis not stated | sample value. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Alaria esculenta2012Basis not stated | mean. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Laminaria digitata2012Basis not stated | mean. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Laminaria digitata2012Basis not stated | sample value. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Laminaria longicruris2012Basis not stated | mean. | ||
| Kombu/kelp · driedTaylor et al. 2016 | Saccharina latissima2012Basis not stated | sample value. | ||
| Kombu/kelp · driedZhao et al. 2014 | Laminaria japonica water extract2012 | sample value. | ||
| Wakame · driedGarcía-Salgado et al. 2012 | Wakame, JapanCollection date unreported | sample value. | ||
| Wakame · driedGarcía-Salgado et al. 2012 | Wakame, SpainCollection date unreported | not detected. | ||
| Wakame · driedHata et al. 2014 | retail dry wakameCollection date unreported | not detected. | ||
| Wakame · driedLlorente-Mirandes et al. 2011 | Undaria pinnatifidaCollection date unreported | sample value. | ||
| Wakame · driedZhao et al. 2014 | Undaria pinnatifida water extract2012 | sample value. | ||
| Arame · driedGarcía-Salgado et al. 2012 | Arame, JapanCollection date unreported | sample value. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region EURO; random sampling2020Dried product as sold | median. | ||
| Nori/laver · driedGarcía-Salgado et al. 2012 | Nori, JapanCollection date unreported | sample value. | ||
| Nori/laver · driedGarcía-Salgado et al. 2012 | Nori, SpainCollection date unreported | not detected. | ||
| Nori/laver · driedLlorente-Mirandes et al. 2011 | Porphyra purpureaCollection date unreported | sample value. | ||
| Nori/laver · driedLorenc et al. 2020 | Sample 3Collection date unreportedBasis not stated | below LOD. | ||
| Nori/laver · driedLorenc et al. 2020 | Sample 3Collection date unreportedBasis not stated | below LOD. | ||
| Nori/laver · driedLorenc et al. 2020 | Sample 3Collection date unreportedBasis not stated | below LOD. | ||
| Nori/laver · driedLorenc et al. 2020 | Sample 3Collection date unreportedBasis not stated | below LOD. | ||
| Nori/laver · driedSim et al. 2024 | P. dioica2020–2022 | mean. | ||
| Nori/laver · driedTaylor et al. 2016 | Porphyra umbilicalus2012Basis not stated | sample value. | ||
| Nori/laver · driedWei et al. 2003 | Porphyra, all five producing areas2001 | not detected. | ||
| Nori/laver · driedZhao et al. 2014 | Porphyra yezoensis water extract2012 | sample value. | ||
| Dulse · driedSim et al. 2024 | P. palmata2020–2022 | mean. | ||
| Dulse · driedTaylor et al. 2016 | Palmaria palmata2012Basis not stated | mean. | ||
| Sea spaghetti · driedGarcía-Salgado et al. 2012 | Sea spaghetti, SpainCollection date unreported | not detected. | ||
| Wracks (Fucus/Ascophyllum) · driedGarcía-Salgado et al. 2012 | Fucus, FranceCollection date unreported | sample value. | ||
| Wracks (Fucus/Ascophyllum) · driedOwnsworth et al. 2019 | Fucus vesiculosusCollection date unreported | range. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | A. nodosum2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | A. nodosum2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | A. nodosum primary shoot2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | A. nodosum primary shoot2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | F. vesiculosus2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedSim et al. 2024 | F. vesiculosus2020–2022 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Ascophyllum nodosum2012Basis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Ascophyllum nodosum2012Basis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Fucus spiralis2012Basis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Fucus vesiculosus2012Basis not stated | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedTaylor et al. 2016 | Fucus vesiculosus2012Basis not stated | mean. | ||
| Carrageen (Irish moss) · driedLlorente-Mirandes et al. 2011 | Chondrus crispusCollection date unreported | below LOD. | ||
| Carrageen (Irish moss) · driedTaylor et al. 2016 | Chondrus crispus2012Basis not stated | sample value. | ||
| Carrageen (Irish moss) · driedTaylor et al. 2016 | Chondrus crispus2012Basis not stated | mean. | ||
| Green seaweeds (Ulva etc.) · driedLlorente-Mirandes et al. 2011 | Ulva rigidaCollection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · driedTaylor et al. 2016 | Chaetomorpha picquotiana2012Basis not stated | sample value. | ||
| Green seaweeds (Ulva etc.) · driedTaylor et al. 2016 | Gayralia oxysperma2012Basis not stated | sample value. | ||
| Green seaweeds (Ulva etc.) · driedTaylor et al. 2016 | Ulva lactuca2012Basis not stated | sample value. | ||
| Green seaweeds (Ulva etc.) · driedTaylor et al. 2016 | Ulva lactuca2012Basis not stated | below LOD. | ||
| Green seaweeds (Ulva etc.) · driedTaylor et al. 2016 | Ulva prolifera2012Basis not stated | sample value. | ||
| Green seaweeds (Ulva etc.) · driedZhao et al. 2014 | Enteromorpha prolifera water2012 | sample value. | ||
| Other brown · driedTaylor et al. 2016 | Colpomenia marina2012Basis not stated | sample value. | ||
| Other red · driedSim et al. 2024 | A. taxiformis2020–2022 | mean. | ||
| Other red · driedSim et al. 2024 | C. purpureum2020–2022 | mean. | ||
| Other red · driedTaylor et al. 2016 | Gracliaria vermiculophylla2012Basis not stated | sample value. | ||
| Other red · driedTaylor et al. 2016 | Heterosiphonia japonica2012Basis not stated | sample value. | ||
| Other red · driedTaylor et al. 2016 | Phyllophora pseudoceranoides2012Basis not stated | sample value. | ||
| Other red · driedTaylor et al. 2016 | Polyiphonia lanosa2012Basis not stated | sample value. | ||
| Mixed or unspecified · driedEFSA et al. 2024 | Algae and prokaryotes organisms2012–2021 | 95th percentile. | ||
| Mixed or unspecified · driedEFSA et al. 2024 | Algae and prokaryotes organisms2012–2021 | 95th percentile. | ||
| Mixed or unspecified · driedEFSA et al. 2024 | Algae and prokaryotes organisms2012–2021 | mean.Same samples: 1,710 µg/kg (95th percentile) | ||
| Mixed or unspecified · driedEFSA et al. 2024 | Algae and prokaryotes organisms2012–2021 | mean. | ||
| Mixed or unspecified · driedTaylor et al. 2016 | Mixed seaweed product "soup1"2012Basis not stated | sample value. | ||
| Mixed or unspecified · driedTaylor et al. 2016 | Mixed seaweed product "soup2"2012Basis not stated | sample value. | ||
10 findings · 2 studies | ||||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Korean variety, Feb 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Korean variety, Jan 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Korean variety, Mar 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Native variety, Apr 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Native variety, Feb 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Native variety, Jan 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Native variety, Mar 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedHuang et al. 2020 | Native variety, May 20162016 | mean. | ||
| Hijiki · fresh or wild-collectedShimoda et al. 2010 | sample 8; Amatsu; not applicable)Collection date unreported | sample value. | ||
| Hijiki · fresh or wild-collectedShimoda et al. 2010 | sample 9Collection date unreported | sample value. | ||
65 findings · 7 studies | ||||
| Hijiki · powderLorenc et al. 2020 | Sample 1Collection date unreportedBasis not stated | below LOD. | ||
| Hijiki · powderLorenc et al. 2020 | Sample 1Collection date unreportedBasis not stated | below LOD. | ||
| Hijiki · powderLorenc et al. 2020 | Sample 1Collection date unreportedBasis not stated | below LOD. | ||
| Hijiki · powderLorenc et al. 2020 | Sample 1Collection date unreportedBasis not stated | below LOD. | ||
| Hijiki · powderNarukawa et al. 2020 | candidate CRM 7405-bCollection date unreported | mean. | ||
| Hijiki · powderNarukawa et al. 2020 | candidate CRM 7405-bCollection date unreported | mean. | ||
| Hijiki · powderNarukawa et al. 2020 | candidate CRM 7405-bCollection date unreported | mean. | ||
| Hijiki · powderNarukawa et al. 2020 | candidate CRM 7405-bCollection date unreported | mean. | ||
| Hijiki · powderNarukawa et al. 2020 | NMIJ CRM 7405-a, Lab 1 condition 1Collection date unreported | mean. | ||
| Hijiki · powderNarukawa et al. 2020 | NMIJ CRM 7405-a, Lab 2 condition 1Collection date unreported | mean. | ||
| Hijiki · powderSim et al. 2024 | Hijiki CRM NMIJ 7405-b2020–2022 | mean. | ||
| Kombu/kelp · powderLorenc et al. 2020 | Sample 5Collection date unreportedBasis not stated | below LOD. | ||
| Kombu/kelp · powderLorenc et al. 2020 | Sample 5Collection date unreportedBasis not stated | below LOD. | ||
| Kombu/kelp · powderNischwitz et al. 2006 | KE10Collection date unreportedDried product as sold | sample value. | ||
| Kombu/kelp · powderNischwitz et al. 2006 | KE7Collection date unreportedDried product as sold | sample value. | ||
| Kombu/kelp · powderNischwitz et al. 2006 | KE7Collection date unreportedDried product as sold | sample value. | ||
| Kombu/kelp · powderNischwitz et al. 2006 | KE7Collection date unreportedDried product as sold | sample value. | ||
| Kombu/kelp · powderNischwitz et al. 2006 | KE8Collection date unreportedDried product as sold | sample value. | ||
| Kombu/kelp · powderNischwitz et al. 2006 | KE9Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderLorenc et al. 2020 | Sample 4Collection date unreportedBasis not stated | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · powderLorenc et al. 2020 | Sample 4Collection date unreportedBasis not stated | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · powderLorenc et al. 2020 | Sample 4Collection date unreportedBasis not stated | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · powderLorenc et al. 2020 | Sample 4Collection date unreportedBasis not stated | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · powderLuvonga et al. 2021 | Kelp powderCollection date unreported | mean. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE1Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE11Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE11Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE11Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE12Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE2Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE2Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE2Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE3Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE4Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE5Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderNischwitz et al. 2006 | KE6Collection date unreportedDried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · powderSiregar et al. 2025 | Fucus vesiculosus2021 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · powderSiregar et al. 2025 | Fucus vesiculosus2021 | mean. | ||
| Wracks (Fucus/Ascophyllum) · powderSiregar et al. 2025 | Fucus vesiculosus2021 | mean. | ||
| Wracks (Fucus/Ascophyllum) · powderSiregar et al. 2025 | Fucus vesiculosus2021 | mean. | ||
| Green seaweeds (Ulva etc.) · powderSim et al. 2024 | Ulva lactuca CRM BCR-2792020–2022 | mean. | ||
| Other brown · powderGarcía-Salgado et al. 2012 | CRM NIES No. 9Collection date unreported | sample value. | ||
| Other brown · powderSiregar et al. 2025 | Cystophora monilifera2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystophora monilifera2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystophora monilifera2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystophora monilifera2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystoseira trinodis2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystoseira trinodis2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Cystoseira trinodis2021 | below LOD. | ||
| Other brown · powderSiregar et al. 2025 | Cystoseira trinodis2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Hormosira banksii2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Hormosira banksii2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Hormosira banksii2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Lobospira bicuspidata2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Lobospira bicuspidata2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Lobospira bicuspidata2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Lobospira bicuspidata2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Pachydictyon paniculatum2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Pachydictyon paniculatum2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Pachydictyon paniculatum2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Pachydictyon paniculatum2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Phylospora comosa2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Phylospora comosa2021 | below LOD. | ||
| Other brown · powderSiregar et al. 2025 | Phylospora comosa2021 | mean. | ||
| Other brown · powderSiregar et al. 2025 | Phylospora comosa2021 | mean. | ||
15 findings · 5 studies | ||||
| Hijiki · form not statedZhao et al. 2025 | control groupCollection date unreported | mean. | ||
| Kombu/kelp · form not statedPark et al. 2005 | Tangle 1Collection date unreportedBasis not stated | sample value. | ||
| Kombu/kelp · form not statedPark et al. 2005 | Tangle 2Collection date unreportedBasis not stated | sample value. | ||
| Nori/laver · form not statedPark et al. 2005 | LaverCollection date unreportedBasis not stated | sample value. | ||
| Green seaweeds (Ulva etc.) · form not statedWHO GEMS/Food | WHO region EURO; random sampling2016 | median. | ||
| Other brown · form not statedWHO GEMS/Food | WHO region EURO; random sampling2016 | median. | ||
| Other brown · form not statedCao et al. 2014 | S. pallidum, Yantai, ShandongCollection date unreportedBasis not stated | sample value. | ||
| Other brown · form not statedPark et al. 2005 | Brown seaweed 1Collection date unreportedBasis not stated | sample value. | ||
| Other brown · form not statedPark et al. 2005 | Brown seaweed 2Collection date unreportedBasis not stated | sample value. | ||
| Other brown · form not statedPark et al. 2005 | Brown seaweed 3Collection date unreportedBasis not stated | sample value. | ||
| Other red · form not statedWHO GEMS/Food | WHO region EURO; random sampling2016 | median. | ||
| Mixed or unspecified · form not statedEFSA et al. 2024 | Algae and prokaryotes organisms2012–2021Basis not stated | 95th percentile. | ||
| Mixed or unspecified · form not statedEFSA et al. 2024 | Algae and prokaryotes organisms2012–2021Basis not stated | 95th percentile. | ||
| Mixed or unspecified · form not statedEFSA et al. 2024 | Algae and prokaryotes organisms2012–2021Basis not stated | mean. | ||
| Mixed or unspecified · form not statedEFSA et al. 2024 | Algae and prokaryotes organisms2012–2021Basis not stated | mean. | ||
19 findings · 2 studies | ||||
| Kombu/kelp · supplementCheyns et al. 2021 | FS282013–2016Dried product as sold | sample value. | ||
| Kombu/kelp · supplementCheyns et al. 2021 | FS292013–2016Dried product as sold | sample value. | ||
| Kombu/kelp · supplementCheyns et al. 2021 | FS302013–2016Dried product as sold | sample value. | ||
| Kombu/kelp · supplementGarcía et al. 2006 | Laminaria digitata capsulesCollection date unreportedBasis not stated | not detected. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS162013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS172013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS182013–2016Dried product as sold | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS192013–2016Dried product as sold | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS202013–2016Dried product as sold | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS212013–2016Dried product as sold | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS222013–2016Dried product as sold | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS232013–2016Dried product as sold | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS242013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS252013–2016Dried product as sold | sample value. | ||
| Wracks (Fucus/Ascophyllum) · supplementCheyns et al. 2021 | FS262013–2016Dried product as sold | below LOD. | ||
| Other red · supplementCheyns et al. 2021 | FS312013–2016Dried product as sold | below LOD. | ||
| Other red · supplementCheyns et al. 2021 | FS322013–2016Dried product as sold | below LOD. | ||
| Other red · supplementCheyns et al. 2021 | FS332013–2016Dried product as sold | below LOD. | ||
| Mixed or unspecified · supplementCheyns et al. 2021 | FS272013–2016Dried product as sold | below LOD. | ||
295 findings · 17 studies · 8 spread figures folded in | ||||
| Hijiki · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Hijiki · driedDuinker et al. 2020 | Sargassum fusiforme2014–2019 | sample value. | ||
| Hijiki · driedAlmela et al. 2002 | retail product 16Collection date unreported | sample value. | ||
| Hijiki · driedAlmela et al. 2002 | retail product 17Collection date unreported | sample value. | ||
| Hijiki · driedAlmela et al. 2002 | retail product 18Collection date unreported | sample value. | ||
| Hijiki · driedMartín-León et al. 2021 | Asia Hijiki2020 | mean. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region EURO; random sampling2014–2019Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region EURO; unknown2011Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region WPRO; targeted sampling2015–2017 | median. | ||
| Kombu/kelp · driedDuinker et al. 2020 | Saccharina spp2014–2019 | mean.Same samples: 150–750 µg/kg (range) | ||
| Kombu/kelp · driedDuinker et al. 2020 | Saccharina spp2014–2019 | median. | ||
| Kombu/kelp · driedDuinker et al. 2020 | Saccharina spp2014–2019 | range. | ||
| Kombu/kelp · driedEFSA 2023 seaweed report | Kombu / Dried product2011–2022Dried product as sold | mean. | ||
| Kombu/kelp · driedEFSA 2023 seaweed report | Kombu / Dried product2011–2022Dried product as sold | mean. | ||
| Kombu/kelp · driedAlmela et al. 2002 | retail product 13Collection date unreported | sample value. | ||
| Kombu/kelp · driedAlmela et al. 2002 | retail product 14Collection date unreported | sample value. | ||
| Kombu/kelp · driedHwang et al. 2010 | Kelp, East production coast2007 | mean. | ||
| Kombu/kelp · driedHwang et al. 2010 | Kelp, South production coast2007 | mean. | ||
| Kombu/kelp · driedHwang et al. 2010 | Kelp, subtotal2007 | mean. | ||
| Kombu/kelp · driedMartín-León et al. 2021 | Asia Kombu2020 | mean. | ||
| Kombu/kelp · driedMartín-León et al. 2021 | Europe Kombu2020 | mean. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-1Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-2Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-3Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-4Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | Japanese Laminaria japonicaCollection date unreported | max. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | RMJKCollection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | Scottish Laminaria digitataCollection date unreported | max. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Farmed; base of blade2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Farmed; distal tip2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Wild2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Wild2018–2021 | mean. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample I: White Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample II: White Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample III: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample IV: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample V: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample VI: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedSong et al. 2017 | Kelp, dry2011–2015Dried product as sold | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 12023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 22023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 32023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | WWT2023 | mean. | ||
| Wakame · driedWHO GEMS/Food | WHO region EURO; random sampling2013–2019Dried product as sold | median. | ||
| Wakame · driedWHO GEMS/Food | WHO region EURO; unknown2011–2012Dried product as sold | median. | ||
| Wakame · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Wakame · driedDuinker et al. 2020 | Undaria pinnatifida2014–2019 | mean.Same samples: 720–4,000 µg/kg (range) | ||
| Wakame · driedDuinker et al. 2020 | Undaria pinnatifida2014–2019 | median. | ||
| Wakame · driedDuinker et al. 2020 | Undaria pinnatifida2014–2019 | range. | ||
| Wakame · driedEFSA 2023 seaweed report | Wakame / Dried product2011–2022Dried product as sold | mean. | ||
| Wakame · driedEFSA 2023 seaweed report | Wakame / Dried product2011–2022Dried product as sold | mean. | ||
| Wakame · driedAlmela et al. 2002 | retail product 10Collection date unreported | sample value. | ||
| Wakame · driedAlmela et al. 2002 | retail product 11Collection date unreported | sample value. | ||
| Wakame · driedAlmela et al. 2002 | retail product 12Collection date unreported | sample value. | ||
| Wakame · driedMartín-León et al. 2021 | Asia Wakame2020 | mean. | ||
| Wakame · driedMartín-León et al. 2021 | Europe Wakame2020 | mean. | ||
| Arame · driedDuinker et al. 2020 | Eisenia bicyclis2014–2019 | sample value. | ||
| Arame · driedAlmela et al. 2002 | retail product 7Collection date unreported | sample value. | ||
| Arame · driedAlmela et al. 2002 | retail product 8Collection date unreported | sample value. | ||
| Arame · driedAlmela et al. 2002 | retail product 9Collection date unreported | sample value. | ||
| Arame · driedMartín-León et al. 2021 | Europe Arame2020 | mean. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region EURO; random sampling2013–2019Dried product as sold | median. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region EURO; unknown2011–2019Dried product as sold | median. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Nori/laver · driedDuinker et al. 2020 | Porphyra spp2014–2019 | mean.Same samples: 410–3,400 µg/kg (range) | ||
| Nori/laver · driedDuinker et al. 2020 | Porphyra spp2014–2019 | median. | ||
| Nori/laver · driedDuinker et al. 2020 | Porphyra spp2014–2019 | range. | ||
| Nori/laver · driedEFSA 2023 seaweed report | Laver / Dried product2011–2022Dried product as sold | mean. | ||
| Nori/laver · driedEFSA 2023 seaweed report | Laver / Dried product2011–2022Dried product as sold | mean. | ||
| Nori/laver · driedAlmela et al. 2002 | retail product 3Collection date unreported | sample value. | ||
| Nori/laver · driedAlmela et al. 2002 | retail product 4Collection date unreported | sample value. | ||
| Nori/laver · driedHwang et al. 2010 | Laver, South production coast2007 | mean. | ||
| Nori/laver · driedHwang et al. 2010 | Laver, subtotal2007 | mean. | ||
| Nori/laver · driedHwang et al. 2010 | Laver, West production coast2007 | mean. | ||
| Nori/laver · driedMartín-León et al. 2021 | Asia Nori2020 | mean. | ||
| Nori/laver · driedMartín-León et al. 2021 | Europe Nori2020 | mean. | ||
| Nori/laver · driedSong et al. 2017 | Purple seaweed2011–2015Basis not stated | mean. | ||
| Dulse · driedEFSA 2023 seaweed report | Dulse / Dried product2011–2022Dried product as sold | mean. | ||
| Dulse · driedEFSA 2023 seaweed report | Dulse / Dried product2011–2022Dried product as sold | mean. | ||
| Dulse · driedAlmela et al. 2002 | retail product 6Collection date unreported | sample value. | ||
| Dulse · driedBehnaz et al. 2016 | Palmaria palmata, Fornæs, Denmark2011 | mean. | ||
| Sea spaghetti · driedEFSA 2023 seaweed report | Sea spaghetti / Dried product2011–2022Dried product as sold | mean. | ||
| Sea spaghetti · driedEFSA 2023 seaweed report | Sea spaghetti / Dried product2011–2022Dried product as sold | mean. | ||
| Sea spaghetti · driedMartín-León et al. 2021 | Europe Sea spaghetti2020 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedEFSA 2023 seaweed report | Rockweed / Dried product2011–2022Dried product as sold | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedEFSA 2023 seaweed report | Rockweed / Dried product2011–2022Dried product as sold | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedAlmela et al. 2002 | retail product 15Collection date unreported | sample value. | ||
| Carrageen (Irish moss) · driedEFSA 2023 seaweed report | Carrageen mosses / Dried product2011–2022Dried product as sold | mean. | ||
| Carrageen (Irish moss) · driedEFSA 2023 seaweed report | Carrageen mosses / Dried product2011–2022Dried product as sold | mean. | ||
| Carrageen (Irish moss) · driedBehnaz et al. 2016 | Chondrus crispus, Fornæs, Denmark2011 | mean. | ||
| Green seaweeds (Ulva etc.) · driedDuinker et al. 2020 | Ulva spp2014–2019 | sample value. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Green algae2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Green algae2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Sea lettuce / Dried product2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Sea lettuce / Dried product2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedAlmela et al. 2002 | retail product 1Collection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · driedAlmela et al. 2002 | retail product 2Collection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · driedAykut et al. 2018 | Kadın Creek2011–2012 | mean.Same samples: 10–190 µg/kg (range) | ||
| Green seaweeds (Ulva etc.) · driedAykut et al. 2018 | Kadın Creek2011–2012 | range. | ||
| Green seaweeds (Ulva etc.) · driedHwang et al. 2010 | Sea lettuce2007 | mean. | ||
| Green seaweeds (Ulva etc.) · driedMartín-León et al. 2021 | Europe Sea lettuce2020 | below LOD. | ||
| Other brown · driedEFSA 2023 seaweed report | Brown algae2011–2022Dried product as sold | mean. | ||
| Other brown · driedEFSA 2023 seaweed report | Brown algae2011–2022Dried product as sold | mean. | ||
| Other brown · driedHwang et al. 2010 | Brown seaweed2007 | mean. | ||
| Other brown · driedHwang et al. 2010 | Brown seaweed2007 | mean. | ||
| Other brown · driedHwang et al. 2010 | Brown seaweed, subtotal2007 | mean. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | all 12 spatial sites2019–2020 | mean. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | all 23 unique homogenised2019–2020 | mean. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Aug 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Dec 20192019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Feb 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Jan 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Jul 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Jun 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Karikari2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Leigh2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Mahanga2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Māhia2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Mākara Beach2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Mar 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | May 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Motuotau Island2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Motuotau Island2019–2020 | mean. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Moutohora Island2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Nov 20192019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Nov 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Oct 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Sep 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Titahi Bay2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Tolaga Bay2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Waihau Bay2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Wellington Harbour2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Wilson Bay2019–2020 | sample value. | ||
| Other brown · driedRodríguez-Rodríguez et al. 2026 | Raw Sargassum composite2024Basis not stated | sample value. | ||
| Other red · driedEFSA 2023 seaweed report | Red alga2011–2022Dried product as sold | mean. | ||
| Other red · driedEFSA 2023 seaweed report | Red alga2011–2022Dried product as sold | mean. | ||
| Other red · driedAziz et al. 2021 | G. tenuistipitata var. liuiCollection date unreported | sample value. | ||
| Other red · driedBehnaz et al. 2016 | Ahnfeltia plicata, Fornæs, Denmark2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Delesseria sanguinea2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Dilsea carnosa, Fornæs, Denmark2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Furcellaria lumbricalis2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Gracilaria vermiculophylla2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Odonthalia dentata2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Phycodrys rubens, Fornæs, Denmark2011 | mean. | ||
| Other red · driedKhandaker et al. 2021 | all Malaysian samples2018 | mean. | ||
| Other red · driedKhandaker et al. 2021 | Kota Belud farm2018 | mean.Same samples: 1,230–1,670 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Kota Belud farm2018 | range. | ||
| Other red · driedKhandaker et al. 2021 | Langkawi farm2018 | mean.Same samples: 1,600–1,950 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Langkawi farm2018 | range. | ||
| Other red · driedKhandaker et al. 2021 | Semporna farm2018 | mean.Same samples: 1,400–2,000 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Semporna farm2018 | range. | ||
| Other red · driedMartín-León et al. 2021 | Europe Starry moss2020 | below LOD. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | pooled dried algae types2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | pooled dried algae types2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedAlmela et al. 2002 | all 18 productsCollection date unreported | range. | ||
| Mixed or unspecified · driedHwang et al. 2010 | All seaweed, final total2007 | mean. | ||
| Mixed or unspecified · driedMartín-León et al. 2021 | Europe Mixed salad2020 | mean. | ||
| Mixed or unspecified · driedOwnsworth et al. 2019 | all macroalgaeCollection date unreported | range. | ||
| Mixed or unspecified · driedOwnsworth et al. 2019 | all Scottish macroalgae studiedCollection date unreported | mean.Same samples: 6.1–920 µg/kg (range) | ||
| Mixed or unspecified · driedOwnsworth et al. 2019 | all Scottish macroalgae studiedCollection date unreported | range. | ||
17 findings · 7 studies | ||||
| Hijiki · form not statedZhao et al. 2025 | control groupCollection date unreported | mean. | ||
| Kombu/kelp · form not statedSong et al. 2017 | Kelp2011–2015Basis not stated | mean. | ||
| Kombu/kelp · form not statedZhao et al. 2016 | Laminaria japonicaCollection date unreportedWet (fresh) weight | range. | ||
| Nori/laver · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Nori/laver · form not statedZhao et al. 2016 | Porphyra teneraCollection date unreported | range. | ||
| Dulse · form not statedEFSA 2023 seaweed report | Dulse / Unspecified2011–2022Basis not stated | mean. | ||
| Dulse · form not statedEFSA 2023 seaweed report | Dulse / Unspecified2011–2022Basis not stated | mean. | ||
| Green seaweeds (Ulva etc.) · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Other brown · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Other red · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Mixed or unspecified · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Mixed or unspecified · form not statedEuropean 2012 | Seaweeds2003–2011Basis not stated | mean. | ||
| Mixed or unspecified · form not statedEuropean 2012 | Seaweeds2003–2011Basis not stated | mean. | ||
| Mixed or unspecified · form not statedEuropean 2012 | Seaweeds2003–2011Basis not stated | mean. | ||
| Mixed or unspecified · form not statedLim et al. 2015 | Seaweed2010–2011Basis not stated | mean. | ||
| Mixed or unspecified · form not statedLim et al. 2015 | Seaweed2010–2011Basis not stated | median. | ||
| Mixed or unspecified · form not statedLim et al. 2015 | Seaweed2010–2011Basis not stated | range. | ||
2 findings · 1 study | ||||
| Kombu/kelp · powder or flakesWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Wakame · powder or flakesWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
158 findings · 6 studies · 23 spread figures folded in | ||||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria digitata2014–2019 | mean.Same samples: 33–1,900 µg/kg (range) | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria digitata2014–2019 | median. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria digitata2014–2019 | range. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria hyperborea2014–2019 | sample value. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Saccharina latissima2014–2019 | mean.Same samples: 160–3,100 µg/kg (range) | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Saccharina latissima2014–2019 | median. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Saccharina latissima2014–2019 | range. | ||
| Kombu/kelp · fresh or wild-collectedEFSA 2023 seaweed report | Kombu / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Kombu/kelp · fresh or wild-collectedEFSA 2023 seaweed report | Kombu / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Kombu/kelp · fresh or wild-collectedSund et al. 2026 | Unprocessed2023 | mean. | ||
| Wakame · fresh or wild-collectedEFSA 2023 seaweed report | Wakame / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wakame · fresh or wild-collectedEFSA 2023 seaweed report | Wakame / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra purpurea2014–2019 | mean.Same samples: 170–1,500 µg/kg (range) | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra purpurea2014–2019 | median. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra purpurea2014–2019 | range. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra umbilicalis2014–2019 | mean.Same samples: 190–1,300 µg/kg (range) | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra umbilicalis2014–2019 | median. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra umbilicalis2014–2019 | range. | ||
| Nori/laver · fresh or wild-collectedEFSA 2023 seaweed report | Laver / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Nori/laver · fresh or wild-collectedEFSA 2023 seaweed report | Laver / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Dulse · fresh or wild-collectedDuinker et al. 2020 | Palmaria palmata2014–2019 | mean.Same samples: 50–1,600 µg/kg (range) | ||
| Dulse · fresh or wild-collectedDuinker et al. 2020 | Palmaria palmata2014–2019 | median. | ||
| Dulse · fresh or wild-collectedDuinker et al. 2020 | Palmaria palmata2014–2019 | range. | ||
| Sea spaghetti · fresh or wild-collectedDuinker et al. 2020 | Himanthalia elongata2014–2019 | mean.Same samples: 390–1,800 µg/kg (range) | ||
| Sea spaghetti · fresh or wild-collectedDuinker et al. 2020 | Himanthalia elongata2014–2019 | median. | ||
| Sea spaghetti · fresh or wild-collectedDuinker et al. 2020 | Himanthalia elongata2014–2019 | range. | ||
| Sea spaghetti · fresh or wild-collectedEFSA 2023 seaweed report | Sea spaghetti / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Sea spaghetti · fresh or wild-collectedEFSA 2023 seaweed report | Sea spaghetti / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Ascophyllum nodosum2014–2019 | mean.Same samples: 160–470 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Ascophyllum nodosum2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Ascophyllum nodosum2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus serratus2014–2019 | mean.Same samples: 880–3,300 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus serratus2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus serratus2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus spiralis2014–2019 | mean.Same samples: 450–1,100 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus spiralis2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus spiralis2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus vesiculosus2014–2019 | mean.Same samples: 410–3,100 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus vesiculosus2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus vesiculosus2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Pelvetia canaliculata2014–2019 | mean.Same samples: 240–360 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Pelvetia canaliculata2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Pelvetia canaliculata2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedEFSA 2023 seaweed report | Rockweed / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedEFSA 2023 seaweed report | Rockweed / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | mean.Same samples: 1,150–4,250 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | mean.Same samples: 1,730–2,340 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | sample value. | ||
| Carrageen (Irish moss) · fresh or wild-collectedDuinker et al. 2020 | Chondrus crispus2014–2019 | mean.Same samples: 140–280 µg/kg (range) | ||
| Carrageen (Irish moss) · fresh or wild-collectedDuinker et al. 2020 | Chondrus crispus2014–2019 | median. | ||
| Carrageen (Irish moss) · fresh or wild-collectedDuinker et al. 2020 | Chondrus crispus2014–2019 | range. | ||
| Carrageen (Irish moss) · fresh or wild-collectedEFSA 2023 seaweed report | Carrageen mosses / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Carrageen (Irish moss) · fresh or wild-collectedEFSA 2023 seaweed report | Carrageen mosses / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Codium fragile2014–2019 | median.Same samples: up to 60 µg/kg (range maximum) | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Codium fragile2014–2019 | below LOD. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Codium fragile2014–2019 | range. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva intestinalis2014–2019 | mean.Same samples: 80–550 µg/kg (range) | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva intestinalis2014–2019 | median. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva intestinalis2014–2019 | range. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva lactuca2014–2019 | mean.Same samples: 80–340 µg/kg (range) | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva lactuca2014–2019 | median. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva lactuca2014–2019 | range. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Green algae2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Green algae2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Sea lettuce / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Sea lettuce / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedSundhar et al. 2023 | C. racemosa RawCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedSundhar et al. 2023 | U. lactuca RawCollection date unreportedWet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Alaria esculenta2014–2019 | mean.Same samples: 300–4,800 µg/kg (range) | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Alaria esculenta2014–2019 | median. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Alaria esculenta2014–2019 | range. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Chorda filum2014–2019 | mean.Same samples: 70–470 µg/kg (range) | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Chorda filum2014–2019 | median. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Chorda filum2014–2019 | range. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Halidrys siliquosa2014–2019 | mean.Same samples: 90–280 µg/kg (range) | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Halidrys siliquosa2014–2019 | median. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Halidrys siliquosa2014–2019 | range. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Sargassum muticum2014–2019 | mean.Same samples: 90–640 µg/kg (range) | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Sargassum muticum2014–2019 | median. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Sargassum muticum2014–2019 | range. | ||
| Other brown · fresh or wild-collectedEFSA 2023 seaweed report | pooled fresh/unprocessed brown2011–2022Wet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedEFSA 2023 seaweed report | pooled fresh/unprocessed brown2011–2022Wet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedGroleau et al. 2025 | seaweed, single sampleCollection date unreportedWet (fresh) weight | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | mean.Same samples: 2,480–7,910 µg/kg (range) | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | median. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | range. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other red · fresh or wild-collectedDuinker et al. 2020 | Vertebrata lanosa2014–2019 | mean.Same samples: 2,100–5,000 µg/kg (range) | ||
| Other red · fresh or wild-collectedDuinker et al. 2020 | Vertebrata lanosa2014–2019 | median. | ||
| Other red · fresh or wild-collectedDuinker et al. 2020 | Vertebrata lanosa2014–2019 | range. | ||
| Other red · fresh or wild-collectedSundhar et al. 2023 | K. aliverzii RawCollection date unreportedWet (fresh) weight | mean. | ||
| Mixed or unspecified · fresh or wild-collectedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Wet (fresh) weight | mean. | ||
| Mixed or unspecified · fresh or wild-collectedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Wet (fresh) weight | mean. | ||
12 findings · 2 studies | ||||
| Kombu/kelp · cookedWang et al. 2020 | Jilin ProvinceCollection date unreportedAs prepared (soaked or cooked) | mean. | ||
| Kombu/kelp · cookedWang et al. 2020 | Other AreaCollection date unreportedAs prepared (soaked or cooked) | mean. | ||
| Kombu/kelp · cookedWang et al. 2020 | Songhua River AreaCollection date unreportedAs prepared (soaked or cooked) | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa BoiledCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa MWCCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa SCTCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca BoiledCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca MWCCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca SCTCollection date unreportedWet (fresh) weight | mean. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii BoiledCollection date unreportedWet (fresh) weight | mean. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii MWCCollection date unreportedWet (fresh) weight | mean. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii SCTCollection date unreportedWet (fresh) weight | mean. | ||
5 findings · 2 studies | ||||
| Nori/laver · salted, seasoned or preparedWHO GEMS/Food | WHO region EURO; random sampling2019Wet product as sold or prepared | median. | ||
| Nori/laver · salted, seasoned or preparedWHO GEMS/Food | WHO region EURO; unknown2011Wet product as sold or prepared | median. | ||
| Mixed or unspecified · salted, seasoned or preparedKim et al. 2023 | Sea algae2021Basis not stated | mean. | ||
| Mixed or unspecified · salted, seasoned or preparedKim et al. 2023 | Sea algae2021Basis not stated | min. | ||
| Mixed or unspecified · salted, seasoned or preparedKim et al. 2023 | Sea algae2021Basis not stated | max. | ||
1 finding · 1 study | ||||
| Nori/laver · roasted or seasonedAlmela et al. 2002 | retail product 5Collection date unreported | sample value. | ||
6 findings · 1 study | ||||
| Green seaweeds (Ulva etc.) · powderNour et al. 2025 | Ulva clathrata2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Padina pavonica2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Sargassum ilicifolium2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Sargassum latifolium2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Turbinaria decurrens2021 | mean. | ||
| Other red · powderNour et al. 2025 | Hypnea musciformis2021 | mean. | ||
1 finding · 1 study | ||||
| Mixed or unspecified · soaked or rehydratedFechner et al. 2022 | Algae2017–2019As prepared (soaked or cooked) | mean. | ||
321 findings · 19 studies · 8 spread figures folded in | ||||
| Hijiki · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Hijiki · driedDuinker et al. 2020 | Sargassum fusiforme2014–2019 | sample value. | ||
| Hijiki · driedAlmela et al. 2002 | retail product 16Collection date unreported | sample value. | ||
| Hijiki · driedAlmela et al. 2002 | retail product 17Collection date unreported | sample value. | ||
| Hijiki · driedAlmela et al. 2002 | retail product 18Collection date unreported | sample value. | ||
| Hijiki · driedMartín-León et al. 2021 | Asia Hijiki2020 | mean. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region EURO; random sampling2014–2019Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region EURO; unknown2003–2011Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region PAHO; random sampling2013 | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region WPRO; random sampling2008–2024Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region WPRO; targeted sampling2015 | median. | ||
| Kombu/kelp · driedDuinker et al. 2020 | Saccharina spp2014–2019 | below LOD. | ||
| Kombu/kelp · driedEFSA 2023 seaweed report | Kombu / Dried product2011–2022Dried product as sold | mean. | ||
| Kombu/kelp · driedEFSA 2023 seaweed report | Kombu / Dried product2011–2022Dried product as sold | mean. | ||
| Kombu/kelp · driedAlmela et al. 2002 | retail product 13Collection date unreported | below LOD. | ||
| Kombu/kelp · driedAlmela et al. 2002 | retail product 14Collection date unreported | below LOD. | ||
| Kombu/kelp · driedHwang et al. 2010 | Kelp, East production coast2007 | mean. | ||
| Kombu/kelp · driedHwang et al. 2010 | Kelp, South production coast2007 | mean. | ||
| Kombu/kelp · driedHwang et al. 2010 | Kelp, subtotal2007 | mean. | ||
| Kombu/kelp · driedMartín-León et al. 2021 | Asia Kombu2020 | mean. | ||
| Kombu/kelp · driedMartín-León et al. 2021 | Europe Kombu2020 | mean. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-1Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-2Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-3Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-4Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | Japanese Laminaria japonicaCollection date unreported | max. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | RMJKCollection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | Scottish Laminaria digitataCollection date unreported | max. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Farmed; base of blade2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Farmed; distal tip2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Wild2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Wild2018–2021 | mean. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample I: White Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample II: White Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample III: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample IV: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample V: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample VI: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 12023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 22023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 32023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | WWT2023 | mean. | ||
| Wakame · driedWHO GEMS/Food | WHO region EURO; random sampling2013–2019Dried product as sold | median. | ||
| Wakame · driedWHO GEMS/Food | WHO region EURO; unknown2011–2012Dried product as sold | median. | ||
| Wakame · driedWHO GEMS/Food | WHO region PAHO; random sampling2013 | median. | ||
| Wakame · driedWHO GEMS/Food | WHO region WPRO; random sampling2012–2024Dried product as sold | median. | ||
| Wakame · driedDuinker et al. 2020 | Undaria pinnatifida2014–2019 | mean.Same samples: up to 1,100 µg/kg (range maximum) | ||
| Wakame · driedDuinker et al. 2020 | Undaria pinnatifida2014–2019 | median. | ||
| Wakame · driedDuinker et al. 2020 | Undaria pinnatifida2014–2019 | range. | ||
| Wakame · driedEFSA 2023 seaweed report | Wakame / Dried product2011–2022Dried product as sold | mean. | ||
| Wakame · driedEFSA 2023 seaweed report | Wakame / Dried product2011–2022Dried product as sold | mean. | ||
| Wakame · driedAlmela et al. 2002 | retail product 10Collection date unreported | below LOD. | ||
| Wakame · driedAlmela et al. 2002 | retail product 11Collection date unreported | below LOD. | ||
| Wakame · driedAlmela et al. 2002 | retail product 12Collection date unreported | below LOD. | ||
| Wakame · driedMartín-León et al. 2021 | Asia Wakame2020 | mean. | ||
| Wakame · driedMartín-León et al. 2021 | Europe Wakame2020 | mean. | ||
| Arame · driedWHO GEMS/Food | WHO region PAHO; random sampling2013 | median. | ||
| Arame · driedDuinker et al. 2020 | Eisenia bicyclis2014–2019 | not detected. | ||
| Arame · driedAlmela et al. 2002 | retail product 7Collection date unreported | sample value. | ||
| Arame · driedAlmela et al. 2002 | retail product 8Collection date unreported | sample value. | ||
| Arame · driedAlmela et al. 2002 | retail product 9Collection date unreported | sample value. | ||
| Arame · driedMartín-León et al. 2021 | Europe Arame2020 | mean. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region EURO; random sampling2013–2019Dried product as sold | median. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region EURO; unknown2005–2019Dried product as sold | median. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region WPRO; random sampling2008–2024Dried product as sold | median. | ||
| Nori/laver · driedDuinker et al. 2020 | Porphyra spp2014–2019 | mean.Same samples: up to 800 µg/kg (range maximum) | ||
| Nori/laver · driedDuinker et al. 2020 | Porphyra spp2014–2019 | median. | ||
| Nori/laver · driedDuinker et al. 2020 | Porphyra spp2014–2019 | range. | ||
| Nori/laver · driedEFSA 2023 seaweed report | Laver / Dried product2011–2022Dried product as sold | mean. | ||
| Nori/laver · driedEFSA 2023 seaweed report | Laver / Dried product2011–2022Dried product as sold | mean. | ||
| Nori/laver · driedAlmela et al. 2002 | retail product 3Collection date unreported | sample value. | ||
| Nori/laver · driedAlmela et al. 2002 | retail product 4Collection date unreported | sample value. | ||
| Nori/laver · driedHwang et al. 2010 | Laver, South production coast2007 | mean. | ||
| Nori/laver · driedHwang et al. 2010 | Laver, subtotal2007 | mean. | ||
| Nori/laver · driedHwang et al. 2010 | Laver, West production coast2007 | mean. | ||
| Nori/laver · driedMartín-León et al. 2021 | Asia Nori2020 | mean. | ||
| Nori/laver · driedMartín-León et al. 2021 | Europe Nori2020 | mean. | ||
| Dulse · driedWHO GEMS/Food | WHO region PAHO; random sampling2013 | median. | ||
| Dulse · driedEFSA 2023 seaweed report | Dulse / Dried product2011–2022Dried product as sold | mean. | ||
| Dulse · driedEFSA 2023 seaweed report | Dulse / Dried product2011–2022Dried product as sold | mean. | ||
| Dulse · driedAlmela et al. 2002 | retail product 6Collection date unreported | sample value. | ||
| Dulse · driedBehnaz et al. 2016 | Palmaria palmata, Fornæs, Denmark2011 | mean. | ||
| Sea spaghetti · driedEFSA 2023 seaweed report | Sea spaghetti / Dried product2011–2022Dried product as sold | mean. | ||
| Sea spaghetti · driedEFSA 2023 seaweed report | Sea spaghetti / Dried product2011–2022Dried product as sold | mean. | ||
| Sea spaghetti · driedMartín-León et al. 2021 | Europe Sea spaghetti2020 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedEFSA 2023 seaweed report | Rockweed / Dried product2011–2022Dried product as sold | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedEFSA 2023 seaweed report | Rockweed / Dried product2011–2022Dried product as sold | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedAlmela et al. 2002 | retail product 15Collection date unreported | sample value. | ||
| Wracks (Fucus/Ascophyllum) · driedOwnsworth et al. 2019 | Fucus vesiculosus, site at 2.85° WCollection date unreported | sample value. | ||
| Carrageen (Irish moss) · driedEFSA 2023 seaweed report | Carrageen mosses / Dried product2011–2022Dried product as sold | mean. | ||
| Carrageen (Irish moss) · driedEFSA 2023 seaweed report | Carrageen mosses / Dried product2011–2022Dried product as sold | mean. | ||
| Carrageen (Irish moss) · driedBehnaz et al. 2016 | Chondrus crispus, Fornæs, Denmark2011 | mean. | ||
| Green seaweeds (Ulva etc.) · driedWHO GEMS/Food | WHO region WPRO; random sampling2012Dried product as sold | median. | ||
| Green seaweeds (Ulva etc.) · driedDuinker et al. 2020 | Ulva spp2014–2019 | sample value. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Green algae2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Green algae2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Sea lettuce / Dried product2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Sea lettuce / Dried product2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedAlmela et al. 2002 | retail product 1Collection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · driedAlmela et al. 2002 | retail product 2Collection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · driedAykut et al. 2018 | Kadın Creek2011–2012 | mean.Same samples: 2,490–8,020 µg/kg (range) | ||
| Green seaweeds (Ulva etc.) · driedAykut et al. 2018 | Kadın Creek2011–2012 | range. | ||
| Green seaweeds (Ulva etc.) · driedHwang et al. 2010 | Sea lettuce2007 | mean. | ||
| Green seaweeds (Ulva etc.) · driedMartín-León et al. 2021 | Europe Sea lettuce2020 | below LOD. | ||
| Green seaweeds (Ulva etc.) · driedRakib et al. 2021 | Chlorophyta2018–2019 | mean. | ||
| Green seaweeds (Ulva etc.) · driedRakib et al. 2021 | G10 Ulva compressa2018–2019 | mean. | ||
| Green seaweeds (Ulva etc.) · driedRakib et al. 2021 | G8 Caulerpa racemosa2018–2019 | mean. | ||
| Green seaweeds (Ulva etc.) · driedRakib et al. 2021 | G9 Enteromorpha intestinalis2018–2019 | mean. | ||
| Other brown · driedEFSA 2023 seaweed report | Brown algae2011–2022Dried product as sold | mean. | ||
| Other brown · driedEFSA 2023 seaweed report | Brown algae2011–2022Dried product as sold | mean. | ||
| Other brown · driedHwang et al. 2010 | Brown seaweed2007 | mean. | ||
| Other brown · driedHwang et al. 2010 | Brown seaweed2007 | mean. | ||
| Other brown · driedHwang et al. 2010 | Brown seaweed, subtotal2007 | mean. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | all 12 spatial sites2019–2020 | mean. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | all 23 unique homogenised2019–2020 | mean. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Aug 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Dec 20192019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Feb 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Jan 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Jul 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Jun 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Karikari2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Leigh2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Mahanga2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Māhia2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Mākara Beach2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Mar 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | May 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Motuotau Island2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Motuotau Island2019–2020 | mean. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Moutohora Island2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Nov 20192019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Nov 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Oct 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Sep 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Titahi Bay2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Tolaga Bay2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Waihau Bay2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Wellington Harbour2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Wilson Bay2019–2020 | sample value. | ||
| Other brown · driedRakib et al. 2021 | B5 Padina tetrastromatica2018–2019 | mean. | ||
| Other brown · driedRakib et al. 2021 | B6 Sargassum oligocystum2018–2019 | mean. | ||
| Other brown · driedRakib et al. 2021 | B7 Padina boryana2018–2019 | mean. | ||
| Other brown · driedRakib et al. 2021 | Phaeophyta2018–2019 | mean. | ||
| Other brown · driedRodríguez-Rodríguez et al. 2026 | Raw Sargassum composite2024Basis not stated | below LOD. | ||
| Other red · driedWHO GEMS/Food | WHO region WPRO; random sampling2012Dried product as sold | median. | ||
| Other red · driedEFSA 2023 seaweed report | Red alga2011–2022Dried product as sold | mean. | ||
| Other red · driedEFSA 2023 seaweed report | Red alga2011–2022Dried product as sold | mean. | ||
| Other red · driedAsni et al. 2020 | dry seasonCollection date unreportedBasis not stated | range. | ||
| Other red · driedAsni et al. 2020 | rainy seasonCollection date unreportedBasis not stated | range. | ||
| Other red · driedAsni et al. 2020 | Station CCollection date unreportedBasis not stated | mean. | ||
| Other red · driedAsni et al. 2020 | Station CCollection date unreportedBasis not stated | mean. | ||
| Other red · driedAziz et al. 2021 | G. tenuistipitata var. liuiCollection date unreported | sample value. | ||
| Other red · driedBehnaz et al. 2016 | Ahnfeltia plicata, Fornæs, Denmark2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Delesseria sanguinea2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Dilsea carnosa, Fornæs, Denmark2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Furcellaria lumbricalis2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Gracilaria vermiculophylla2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Odonthalia dentata2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Phycodrys rubens, Fornæs, Denmark2011 | mean. | ||
| Other red · driedKhandaker et al. 2021 | all Malaysian samples2018 | mean. | ||
| Other red · driedKhandaker et al. 2021 | Kota Belud farm2018 | mean.Same samples: 9,760–11,900 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Kota Belud farm2018 | range. | ||
| Other red · driedKhandaker et al. 2021 | Langkawi farm2018 | mean.Same samples: 6,750–11,000 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Langkawi farm2018 | range. | ||
| Other red · driedKhandaker et al. 2021 | Semporna farm2018 | mean.Same samples: 2,750–4,750 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Semporna farm2018 | range. | ||
| Other red · driedMartín-León et al. 2021 | Europe Starry moss2020 | below LOD. | ||
| Other red · driedRakib et al. 2021 | R1 Hypnea musciformis2018–2019 | mean. | ||
| Other red · driedRakib et al. 2021 | R2 Hypnea pannosa2018–2019 | mean. | ||
| Other red · driedRakib et al. 2021 | R3 Jania rubens2018–2019 | mean. | ||
| Other red · driedRakib et al. 2021 | R4 Gelidium pusillum2018–2019 | mean. | ||
| Other red · driedRakib et al. 2021 | Rhodophyta2018–2019 | mean. | ||
| Mixed or unspecified · driedWHO GEMS/Food | WHO region PAHO; random sampling2013 | median. | ||
| Mixed or unspecified · driedWHO GEMS/Food | WHO region WPRO; random sampling2008–2013Dried product as sold | median. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | pooled dried algae types2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | pooled dried algae types2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedAlmela et al. 2002 | all 18 productsCollection date unreported | range. | ||
| Mixed or unspecified · driedHwang et al. 2010 | All seaweed, final total2007 | mean. | ||
| Mixed or unspecified · driedMartín-León et al. 2021 | Europe Mixed salad2020 | mean. | ||
| Mixed or unspecified · driedOwnsworth et al. 2019 | all macroalgaeCollection date unreported | range. | ||
| Mixed or unspecified · driedOwnsworth et al. 2019 | all Scottish macroalgae studiedCollection date unreported | mean.Same samples: 46–4,100 µg/kg (range) | ||
| Mixed or unspecified · driedOwnsworth et al. 2019 | all Scottish macroalgae studiedCollection date unreported | range. | ||
| Mixed or unspecified · driedRakib et al. 2021 | mean of 10 species2018–2019 | mean. | ||
| Mixed or unspecified · driedWang et al. 2019 | Algae2011–2017Dried product as sold | 95th percentile. | ||
| Mixed or unspecified · driedWang et al. 2019 | Algae2011–2017Dried product as sold | mean.Same samples: 894 µg/kg (95th percentile) | ||
| Mixed or unspecified · driedWang et al. 2019 | Algae2011–2017Dried product as sold | median. | ||
26 findings · 6 studies | ||||
| Hijiki · form not statedZhao et al. 2025 | control groupCollection date unreported | mean. | ||
| Kombu/kelp · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2008–2012As sold, moisture not stated | median. | ||
| Kombu/kelp · form not statedZhao et al. 2016 | Laminaria japonicaCollection date unreportedWet (fresh) weight | range. | ||
| Wakame · form not statedEFSA 2010 | category 142003–2009Basis not stated | sample value. | ||
| Nori/laver · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Nori/laver · form not statedZhao et al. 2016 | Porphyra teneraCollection date unreported | range. | ||
| Dulse · form not statedEFSA 2023 seaweed report | Dulse / Unspecified2011–2022Basis not stated | mean. | ||
| Dulse · form not statedEFSA 2023 seaweed report | Dulse / Unspecified2011–2022Basis not stated | mean. | ||
| Green seaweeds (Ulva etc.) · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2008–2024As sold, moisture not stated | median. | ||
| Other brown · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Other red · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2012–2024As sold, moisture not stated | median. | ||
| Mixed or unspecified · form not statedWHO GEMS/Food | WHO region PAHO; random sampling2013 | median. | ||
| Mixed or unspecified · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2008–2024As sold, moisture not stated | median. | ||
| Mixed or unspecified · form not statedEFSA 2010 | Algae as food2003–2009Basis not stated | 5th percentile. | ||
| Mixed or unspecified · form not statedEFSA 2010 | Algae as food2003–2009Basis not stated | 5th percentile. | ||
| Mixed or unspecified · form not statedEFSA 2010 | Algae as food2003–2009Basis not stated | 95th percentile. | ||
| Mixed or unspecified · form not statedEFSA 2010 | Algae as food2003–2009Basis not stated | 95th percentile. | ||
| Mixed or unspecified · form not statedEFSA 2010 | Algae as food2003–2009Basis not stated | mean. | ||
| Mixed or unspecified · form not statedEFSA 2010 | Algae as food2003–2009Basis not stated | mean. | ||
| Mixed or unspecified · form not statedEFSA 2010 | Algae as food2003–2009Basis not stated | median. | ||
| Mixed or unspecified · form not statedEFSA 2010 | Algae as food2003–2009Basis not stated | median. | ||
| Mixed or unspecified · form not statedEFSA 2010 | Algae as food2003–2009Basis not stated | max. | ||
| Mixed or unspecified · form not statedEFSA 2010 | Algae as food2003–2009Basis not stated | max. | ||
| Mixed or unspecified · form not statedLim et al. 2015 | Seaweed2010–2011Basis not stated | mean. | ||
| Mixed or unspecified · form not statedLim et al. 2015 | Seaweed2010–2011Basis not stated | median. | ||
| Mixed or unspecified · form not statedLim et al. 2015 | Seaweed2010–2011Basis not stated | range. | ||
3 findings · 1 study | ||||
| Kombu/kelp · powder or flakesWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Wakame · powder or flakesWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Mixed or unspecified · powder or flakesWHO GEMS/Food | WHO region WPRO; random sampling2012Dried product as sold | median. | ||
11 findings · 2 studies | ||||
| Kombu/kelp · salted, seasoned or preparedWHO GEMS/Food | WHO region WPRO; random sampling2008Wet product as sold or prepared | median. | ||
| Nori/laver · salted, seasoned or preparedWHO GEMS/Food | WHO region EURO; random sampling2019Wet product as sold or prepared | median. | ||
| Nori/laver · salted, seasoned or preparedWHO GEMS/Food | WHO region EURO; unknown2011Wet product as sold or prepared | median. | ||
| Nori/laver · salted, seasoned or preparedWHO GEMS/Food | WHO region WPRO; random sampling2008–2013Wet product as sold or prepared | median. | ||
| Green seaweeds (Ulva etc.) · salted, seasoned or preparedWHO GEMS/Food | WHO region WPRO; random sampling2008–2013Wet product as sold or prepared | median. | ||
| Other red · salted, seasoned or preparedWHO GEMS/Food | WHO region WPRO; random sampling2008–2013Wet product as sold or prepared | median. | ||
| Mixed or unspecified · salted, seasoned or preparedWHO GEMS/Food | WHO region PAHO; random sampling2013–2014 | median. | ||
| Mixed or unspecified · salted, seasoned or preparedWHO GEMS/Food | WHO region WPRO; random sampling2008–2013Wet product as sold or prepared | median. | ||
| Mixed or unspecified · salted, seasoned or preparedKim et al. 2023 | Sea algae2021Basis not stated | mean. | ||
| Mixed or unspecified · salted, seasoned or preparedKim et al. 2023 | Sea algae2021Basis not stated | min. | ||
| Mixed or unspecified · salted, seasoned or preparedKim et al. 2023 | Sea algae2021Basis not stated | max. | ||
157 findings · 7 studies · 21 spread figures folded in | ||||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria digitata2014–2019 | mean.Same samples: up to 640 µg/kg (range maximum) | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria digitata2014–2019 | median. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria digitata2014–2019 | range. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria hyperborea2014–2019 | not detected. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Saccharina latissima2014–2019 | mean.Same samples: up to 5,700 µg/kg (range maximum) | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Saccharina latissima2014–2019 | median. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Saccharina latissima2014–2019 | range. | ||
| Kombu/kelp · fresh or wild-collectedEFSA 2023 seaweed report | Kombu / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Kombu/kelp · fresh or wild-collectedEFSA 2023 seaweed report | Kombu / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Kombu/kelp · fresh or wild-collectedSund et al. 2026 | Unprocessed2023 | mean. | ||
| Wakame · fresh or wild-collectedEFSA 2023 seaweed report | Wakame / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wakame · fresh or wild-collectedEFSA 2023 seaweed report | Wakame / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra purpurea2014–2019 | mean.Same samples: 55–440 µg/kg (range) | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra purpurea2014–2019 | median. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra purpurea2014–2019 | range. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra umbilicalis2014–2019 | mean.Same samples: up to 840 µg/kg (range maximum) | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra umbilicalis2014–2019 | median. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra umbilicalis2014–2019 | range. | ||
| Nori/laver · fresh or wild-collectedEFSA 2023 seaweed report | Laver / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Nori/laver · fresh or wild-collectedEFSA 2023 seaweed report | Laver / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Dulse · fresh or wild-collectedDuinker et al. 2020 | Palmaria palmata2014–2019 | mean.Same samples: up to 1,100 µg/kg (range maximum) | ||
| Dulse · fresh or wild-collectedDuinker et al. 2020 | Palmaria palmata2014–2019 | median. | ||
| Dulse · fresh or wild-collectedDuinker et al. 2020 | Palmaria palmata2014–2019 | range. | ||
| Sea spaghetti · fresh or wild-collectedDuinker et al. 2020 | Himanthalia elongata2014–2019 | below LOD. | ||
| Sea spaghetti · fresh or wild-collectedEFSA 2023 seaweed report | Sea spaghetti / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Sea spaghetti · fresh or wild-collectedEFSA 2023 seaweed report | Sea spaghetti / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Ascophyllum nodosum2014–2019 | mean.Same samples: up to 1,900 µg/kg (range maximum) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Ascophyllum nodosum2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Ascophyllum nodosum2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus serratus2014–2019 | mean.Same samples: up to 1,700 µg/kg (range maximum) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus serratus2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus serratus2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus spiralis2014–2019 | mean.Same samples: 270–400 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus spiralis2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus spiralis2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus vesiculosus2014–2019 | mean.Same samples: up to 3,300 µg/kg (range maximum) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus vesiculosus2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus vesiculosus2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Pelvetia canaliculata2014–2019 | mean.Same samples: up to 750 µg/kg (range maximum) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Pelvetia canaliculata2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Pelvetia canaliculata2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedEFSA 2023 seaweed report | Rockweed / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedEFSA 2023 seaweed report | Rockweed / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | mean.Same samples: up to 13,200 µg/kg (range maximum) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | mean.Same samples: up to 13,400 µg/kg (range maximum) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | sample value. | ||
| Carrageen (Irish moss) · fresh or wild-collectedDuinker et al. 2020 | Chondrus crispus2014–2019 | mean.Same samples: 300–410 µg/kg (range) | ||
| Carrageen (Irish moss) · fresh or wild-collectedDuinker et al. 2020 | Chondrus crispus2014–2019 | median. | ||
| Carrageen (Irish moss) · fresh or wild-collectedDuinker et al. 2020 | Chondrus crispus2014–2019 | range. | ||
| Carrageen (Irish moss) · fresh or wild-collectedEFSA 2023 seaweed report | Carrageen mosses / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Carrageen (Irish moss) · fresh or wild-collectedEFSA 2023 seaweed report | Carrageen mosses / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Codium fragile2014–2019 | mean.Same samples: 400–2,300 µg/kg (range) | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Codium fragile2014–2019 | median. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Codium fragile2014–2019 | range. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva intestinalis2014–2019 | mean.Same samples: 210–3,000 µg/kg (range) | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva intestinalis2014–2019 | median. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva intestinalis2014–2019 | range. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva lactuca2014–2019 | mean.Same samples: up to 2,800 µg/kg (range maximum) | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva lactuca2014–2019 | median. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva lactuca2014–2019 | range. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Green algae2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Green algae2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Sea lettuce / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Sea lettuce / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedSundhar et al. 2023 | C. racemosa RawCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedSundhar et al. 2023 | U. lactuca RawCollection date unreportedWet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Alaria esculenta2014–2019 | mean.Same samples: up to 4,400 µg/kg (range maximum) | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Alaria esculenta2014–2019 | median. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Alaria esculenta2014–2019 | range. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Chorda filum2014–2019 | mean.Same samples: up to 520 µg/kg (range maximum) | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Chorda filum2014–2019 | median. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Chorda filum2014–2019 | range. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Halidrys siliquosa2014–2019 | mean.Same samples: 24–540 µg/kg (range) | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Halidrys siliquosa2014–2019 | median. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Halidrys siliquosa2014–2019 | range. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Sargassum muticum2014–2019 | sample value. | ||
| Other brown · fresh or wild-collectedEFSA 2023 seaweed report | pooled fresh/unprocessed brown2011–2022Wet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedEFSA 2023 seaweed report | pooled fresh/unprocessed brown2011–2022Wet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedGroleau et al. 2025 | seaweed, single sampleCollection date unreportedWet (fresh) weight | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | mean.Same samples: up to 140 µg/kg (range maximum) | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | median. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | range. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other red · fresh or wild-collectedDuinker et al. 2020 | Vertebrata lanosa2014–2019 | mean.Same samples: 240–3,300 µg/kg (range) | ||
| Other red · fresh or wild-collectedDuinker et al. 2020 | Vertebrata lanosa2014–2019 | median. | ||
| Other red · fresh or wild-collectedDuinker et al. 2020 | Vertebrata lanosa2014–2019 | range. | ||
| Other red · fresh or wild-collectedSundhar et al. 2023 | K. aliverzii RawCollection date unreportedWet (fresh) weight | mean. | ||
| Mixed or unspecified · fresh or wild-collectedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Wet (fresh) weight | mean. | ||
| Mixed or unspecified · fresh or wild-collectedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Wet (fresh) weight | mean. | ||
| Mixed or unspecified · fresh or wild-collectedRakib et al. 2021 | mean of 10 species2018–2019Wet (fresh) weight | mean. | ||
12 findings · 2 studies | ||||
| Kombu/kelp · cookedWang et al. 2020 | Jilin ProvinceCollection date unreportedAs prepared (soaked or cooked) | mean. | ||
| Kombu/kelp · cookedWang et al. 2020 | Other AreaCollection date unreportedAs prepared (soaked or cooked) | mean. | ||
| Kombu/kelp · cookedWang et al. 2020 | Songhua River AreaCollection date unreportedAs prepared (soaked or cooked) | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa BoiledCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa MWCCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa SCTCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca BoiledCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca MWCCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca SCTCollection date unreportedWet (fresh) weight | mean. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii BoiledCollection date unreportedWet (fresh) weight | mean. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii MWCCollection date unreportedWet (fresh) weight | mean. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii SCTCollection date unreportedWet (fresh) weight | not detected. | ||
2 findings · 1 study | ||||
| Wakame · freshWHO GEMS/Food | WHO region PAHO; random sampling2013 | median. | ||
| Mixed or unspecified · freshWHO GEMS/Food | WHO region WPRO; random sampling2008–2013Wet product as sold or prepared | median. | ||
4 findings · 1 study | ||||
| Nori/laver · roasted or seasoned snackWHO GEMS/Food | WHO region PAHO; random sampling2013–2014 | median. | ||
| Nori/laver · roasted or seasoned snackWHO GEMS/Food | WHO region WPRO; random sampling2008–2013Dried product as sold | median. | ||
| Mixed or unspecified · roasted or seasoned snackWHO GEMS/Food | WHO region PAHO; random sampling2013 | median. | ||
| Mixed or unspecified · roasted or seasoned snackWHO GEMS/Food | WHO region WPRO; random sampling2008–2013Dried product as sold | median. | ||
1 finding · 1 study | ||||
| Nori/laver · roasted or seasonedAlmela et al. 2002 | retail product 5Collection date unreported | sample value. | ||
6 findings · 1 study | ||||
| Green seaweeds (Ulva etc.) · powderNour et al. 2025 | Ulva clathrata2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Padina pavonica2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Sargassum ilicifolium2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Sargassum latifolium2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Turbinaria decurrens2021 | mean. | ||
| Other red · powderNour et al. 2025 | Hypnea musciformis2021 | mean. | ||
2 findings · 1 study | ||||
| Other red · frozenWHO GEMS/Food | WHO region WPRO; random sampling2012Wet product as sold or prepared | median. | ||
| Mixed or unspecified · frozenWHO GEMS/Food | WHO region WPRO; random sampling2012–2013Wet product as sold or prepared | median. | ||
1 finding · 1 study | ||||
| Mixed or unspecified · soaked or rehydratedFechner et al. 2022 | Algae2017–2019As prepared (soaked or cooked) | mean. | ||
272 findings · 13 studies | ||||
| Hijiki · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Hijiki · driedDuinker et al. 2020 | Sargassum fusiforme2014–2019 | not detected. | ||
| Hijiki · driedAlmela et al. 2002 | retail product 16Collection date unreported | sample value. | ||
| Hijiki · driedAlmela et al. 2002 | retail product 17Collection date unreported | sample value. | ||
| Hijiki · driedAlmela et al. 2002 | retail product 18Collection date unreported | sample value. | ||
| Hijiki · driedMartín-León et al. 2021 | Asia Hijiki2020 | mean. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region EURO; random sampling2011–2017Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region EURO; unknown2011–2013Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region WPRO; targeted sampling2015 | median. | ||
| Kombu/kelp · driedDuinker et al. 2020 | Saccharina spp2014–2019 | below LOD. | ||
| Kombu/kelp · driedDuinker et al. 2020 | Saccharina spp2014–2019 | below LOD. | ||
| Kombu/kelp · driedEFSA 2023 seaweed report | Kombu / Dried product2011–2022Dried product as sold | mean. | ||
| Kombu/kelp · driedEFSA 2023 seaweed report | Kombu / Dried product2011–2022Dried product as sold | mean. | ||
| Kombu/kelp · driedAlmela et al. 2002 | retail product 13Collection date unreported | sample value. | ||
| Kombu/kelp · driedAlmela et al. 2002 | retail product 14Collection date unreported | sample value. | ||
| Kombu/kelp · driedHwang et al. 2010 | Kelp, East production coast2007 | mean. | ||
| Kombu/kelp · driedHwang et al. 2010 | Kelp, South production coast2007 | mean. | ||
| Kombu/kelp · driedHwang et al. 2010 | Kelp, subtotal2007 | mean. | ||
| Kombu/kelp · driedMartín-León et al. 2021 | Asia Kombu2020 | mean. | ||
| Kombu/kelp · driedMartín-León et al. 2021 | Europe Kombu2020 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Farmed; base of blade2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Farmed; distal tip2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Wild2018–2021 | mean. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Wild2018–2021 | mean. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample I: White Sea2014–2016 | below LOD. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample II: White Sea2014–2016 | below LOD. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample III: Yellow Sea2014–2016 | below LOD. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample IV: Yellow Sea2014–2016 | below LOD. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample V: Yellow Sea2014–2016 | below LOD. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample VI: Yellow Sea2014–2016 | below LOD. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 12023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 22023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 32023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | WWT2023 | mean. | ||
| Wakame · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Wakame · driedDuinker et al. 2020 | Undaria pinnatifida2014–2019 | below LOD. | ||
| Wakame · driedDuinker et al. 2020 | Undaria pinnatifida2014–2019 | below LOD. | ||
| Wakame · driedEFSA 2023 seaweed report | Wakame / Dried product2011–2022Dried product as sold | mean. | ||
| Wakame · driedEFSA 2023 seaweed report | Wakame / Dried product2011–2022Dried product as sold | mean. | ||
| Wakame · driedAlmela et al. 2002 | retail product 10Collection date unreported | sample value. | ||
| Wakame · driedAlmela et al. 2002 | retail product 11Collection date unreported | sample value. | ||
| Wakame · driedAlmela et al. 2002 | retail product 12Collection date unreported | sample value. | ||
| Wakame · driedMartín-León et al. 2021 | Asia Wakame2020 | mean. | ||
| Wakame · driedMartín-León et al. 2021 | Europe Wakame2020 | mean. | ||
| Arame · driedDuinker et al. 2020 | Eisenia bicyclis2014–2019 | not detected. | ||
| Arame · driedAlmela et al. 2002 | retail product 7Collection date unreported | sample value. | ||
| Arame · driedAlmela et al. 2002 | retail product 8Collection date unreported | sample value. | ||
| Arame · driedAlmela et al. 2002 | retail product 9Collection date unreported | sample value. | ||
| Arame · driedMartín-León et al. 2021 | Europe Arame2020 | mean. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region EURO; random sampling2013–2014Dried product as sold | median. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region EURO; unknown2011–2012Dried product as sold | median. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Nori/laver · driedDuinker et al. 2020 | Porphyra spp2014–2019 | below LOD. | ||
| Nori/laver · driedDuinker et al. 2020 | Porphyra spp2014–2019 | below LOD. | ||
| Nori/laver · driedEFSA 2023 seaweed report | Laver / Dried product2011–2022Dried product as sold | mean. | ||
| Nori/laver · driedEFSA 2023 seaweed report | Laver / Dried product2011–2022Dried product as sold | mean. | ||
| Nori/laver · driedAlmela et al. 2002 | retail product 3Collection date unreported | sample value. | ||
| Nori/laver · driedAlmela et al. 2002 | retail product 4Collection date unreported | sample value. | ||
| Nori/laver · driedHwang et al. 2010 | Laver, South production coast2007 | mean. | ||
| Nori/laver · driedHwang et al. 2010 | Laver, subtotal2007 | mean. | ||
| Nori/laver · driedHwang et al. 2010 | Laver, West production coast2007 | mean. | ||
| Nori/laver · driedMartín-León et al. 2021 | Asia Nori2020 | mean. | ||
| Nori/laver · driedMartín-León et al. 2021 | Europe Nori2020 | mean. | ||
| Dulse · driedEFSA 2023 seaweed report | Dulse / Dried product2011–2022Dried product as sold | mean. | ||
| Dulse · driedEFSA 2023 seaweed report | Dulse / Dried product2011–2022Dried product as sold | mean. | ||
| Dulse · driedAlmela et al. 2002 | retail product 6Collection date unreported | sample value. | ||
| Sea spaghetti · driedEFSA 2023 seaweed report | Sea spaghetti / Dried product2011–2022Dried product as sold | mean. | ||
| Sea spaghetti · driedEFSA 2023 seaweed report | Sea spaghetti / Dried product2011–2022Dried product as sold | mean. | ||
| Sea spaghetti · driedMartín-León et al. 2021 | Europe Sea spaghetti2020 | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedEFSA 2023 seaweed report | Rockweed / Dried product2011–2022Dried product as sold | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedEFSA 2023 seaweed report | Rockweed / Dried product2011–2022Dried product as sold | mean. | ||
| Wracks (Fucus/Ascophyllum) · driedAlmela et al. 2002 | retail product 15Collection date unreported | sample value. | ||
| Carrageen (Irish moss) · driedEFSA 2023 seaweed report | Carrageen mosses / Dried product2011–2022Dried product as sold | mean. | ||
| Carrageen (Irish moss) · driedEFSA 2023 seaweed report | Carrageen mosses / Dried product2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedDuinker et al. 2020 | Ulva spp2014–2019 | not detected. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Green algae2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Green algae2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Sea lettuce / Dried product2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedEFSA 2023 seaweed report | Sea lettuce / Dried product2011–2022Dried product as sold | mean. | ||
| Green seaweeds (Ulva etc.) · driedAlmela et al. 2002 | retail product 1Collection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · driedAlmela et al. 2002 | retail product 2Collection date unreported | sample value. | ||
| Green seaweeds (Ulva etc.) · driedAykut et al. 2018 | Kadın Creek2011–2012 | mean. | ||
| Green seaweeds (Ulva etc.) · driedAykut et al. 2018 | Kadın Creek2011–2012 | range. | ||
| Green seaweeds (Ulva etc.) · driedHwang et al. 2010 | Sea lettuce2007 | mean. | ||
| Green seaweeds (Ulva etc.) · driedMartín-León et al. 2021 | Europe Sea lettuce2020 | below LOD. | ||
| Other brown · driedEFSA 2023 seaweed report | Brown algae2011–2022Dried product as sold | mean. | ||
| Other brown · driedEFSA 2023 seaweed report | Brown algae2011–2022Dried product as sold | mean. | ||
| Other brown · driedHwang et al. 2010 | Brown seaweed2007 | mean. | ||
| Other brown · driedHwang et al. 2010 | Brown seaweed2007 | mean. | ||
| Other brown · driedHwang et al. 2010 | Brown seaweed, subtotal2007 | mean. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | all 12 spatial sites2019–2020 | mean. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | all 23 unique homogenised2019–2020 | mean. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Aug 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Dec 20192019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Feb 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Jan 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Jul 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Jun 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Karikari2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Leigh2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Mahanga2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Māhia2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Mākara Beach2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Mar 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | May 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Motuotau Island2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Motuotau Island2019–2020 | mean. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Moutohora Island2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Nov 20192019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Nov 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Oct 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Sep 20202019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Titahi Bay2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Tolaga Bay2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Waihau Bay2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Wellington Harbour2019–2020 | sample value. | ||
| Other brown · driedNepper-Davidsen et al. 2023 | Wilson Bay2019–2020 | sample value. | ||
| Other brown · driedRodríguez-Rodríguez et al. 2026 | Raw Sargassum composite2024Basis not stated | below LOD. | ||
| Other red · driedEFSA 2023 seaweed report | Red alga2011–2022Dried product as sold | mean. | ||
| Other red · driedEFSA 2023 seaweed report | Red alga2011–2022Dried product as sold | mean. | ||
| Other red · driedMartín-León et al. 2021 | Europe Starry moss2020 | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | pooled dried algae types2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedEFSA 2023 seaweed report | pooled dried algae types2011–2022Dried product as sold | mean. | ||
| Mixed or unspecified · driedAlmela et al. 2002 | all 18 productsCollection date unreported | range. | ||
| Mixed or unspecified · driedCardoso et al. 2023 | Ria de Aveiro, flora average2019–2020Basis not stated | mean. | ||
| Mixed or unspecified · driedCardoso et al. 2023 | Ria Formosa, flora average2019–2020Basis not stated | mean. | ||
| Mixed or unspecified · driedCardoso et al. 2023 | Tagus estuary, flora average2019–2020Basis not stated | mean. | ||
| Mixed or unspecified · driedHwang et al. 2010 | All seaweed, final total2007 | mean. | ||
| Mixed or unspecified · driedMartín-León et al. 2021 | Europe Mixed salad2020 | mean. | ||
2 findings · 1 study | ||||
| Kombu/kelp · powder or flakesWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Wakame · powder or flakesWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
221 findings · 8 studies · 9 spread figures folded in | ||||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria digitata2014–2019 | mean.Same samples: up to 67 µg/kg (range maximum) | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria digitata2014–2019 | median. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria digitata2014–2019 | range. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Laminaria hyperborea2014–2019 | not detected. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Saccharina latissima2014–2019 | below LOD. | ||
| Kombu/kelp · fresh or wild-collectedDuinker et al. 2020 | Saccharina latissima2014–2019 | range. | ||
| Kombu/kelp · fresh or wild-collectedEFSA 2023 seaweed report | Kombu / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Kombu/kelp · fresh or wild-collectedEFSA 2023 seaweed report | Kombu / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Kombu/kelp · fresh or wild-collectedSund et al. 2026 | Unprocessed2023 | mean. | ||
| Wakame · fresh or wild-collectedEFSA 2023 seaweed report | Wakame / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wakame · fresh or wild-collectedEFSA 2023 seaweed report | Wakame / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra purpurea2014–2019 | mean.Same samples: up to 7 µg/kg (range maximum) | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra purpurea2014–2019 | median. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra purpurea2014–2019 | range. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra umbilicalis2014–2019 | below LOD. | ||
| Nori/laver · fresh or wild-collectedDuinker et al. 2020 | Porphyra umbilicalis2014–2019 | range. | ||
| Nori/laver · fresh or wild-collectedEFSA 2023 seaweed report | Laver / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Nori/laver · fresh or wild-collectedEFSA 2023 seaweed report | Laver / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Dulse · fresh or wild-collectedDuinker et al. 2020 | Palmaria palmata2014–2019 | below LOD. | ||
| Dulse · fresh or wild-collectedDuinker et al. 2020 | Palmaria palmata2014–2019 | range. | ||
| Sea spaghetti · fresh or wild-collectedDuinker et al. 2020 | Himanthalia elongata2014–2019 | below LOD. | ||
| Sea spaghetti · fresh or wild-collectedDuinker et al. 2020 | Himanthalia elongata2014–2019 | below LOD. | ||
| Sea spaghetti · fresh or wild-collectedEFSA 2023 seaweed report | Sea spaghetti / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Sea spaghetti · fresh or wild-collectedEFSA 2023 seaweed report | Sea spaghetti / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Ascophyllum nodosum2014–2019 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Ascophyllum nodosum2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus serratus2014–2019 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus serratus2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus spiralis2014–2019 | mean.Same samples: up to 5 µg/kg (range maximum) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus spiralis2014–2019 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus spiralis2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus vesiculosus2014–2019 | mean.Same samples: up to 22 µg/kg (range maximum) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus vesiculosus2014–2019 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Fucus vesiculosus2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Pelvetia canaliculata2014–2019 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedDuinker et al. 2020 | Pelvetia canaliculata2014–2019 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedEFSA 2023 seaweed report | Rockweed / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedEFSA 2023 seaweed report | Rockweed / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro2019–2020Wet (fresh) weight | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro2019–2020Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro, Ovar, Au2019–2020Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro, Torreira, Au2019–2020Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary2019–2020Wet (fresh) weight | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Samouco, Au2019–2020Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Samouco, Sp2019–2020Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Samouco, Su2019–2020Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Samouco, Wi2019–2020Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Seixal, Su2019–2020Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Seixal, Wi2019–2020Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Trancao, Au2019–2020Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Trancao, Sp2019–2020Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Trancao, Su2019–2020Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Trancao, Wi2019–2020Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | mean.Same samples: up to 210 µg/kg (range maximum) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHarding et al. 2018 | Bladder wrack2003Wet (fresh) weight | mean.Same samples: 6–6.3 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHarding et al. 2018 | Bladder wrack2003Wet (fresh) weight | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHarding et al. 2018 | Bladder wrack2003Wet (fresh) weight | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHarding et al. 2018 | Knotted wrack2003Wet (fresh) weight | mean.Same samples: 11.2–13.1 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHarding et al. 2018 | Knotted wrack2003Wet (fresh) weight | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHarding et al. 2018 | Knotted wrack2003Wet (fresh) weight | range. | ||
| Carrageen (Irish moss) · fresh or wild-collectedDuinker et al. 2020 | Chondrus crispus2014–2019 | mean.Same samples: 5–7 µg/kg (range) | ||
| Carrageen (Irish moss) · fresh or wild-collectedDuinker et al. 2020 | Chondrus crispus2014–2019 | median. | ||
| Carrageen (Irish moss) · fresh or wild-collectedDuinker et al. 2020 | Chondrus crispus2014–2019 | range. | ||
| Carrageen (Irish moss) · fresh or wild-collectedEFSA 2023 seaweed report | Carrageen mosses / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Carrageen (Irish moss) · fresh or wild-collectedEFSA 2023 seaweed report | Carrageen mosses / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Codium fragile2014–2019 | below LOD. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Codium fragile2014–2019 | below LOD. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva intestinalis2014–2019 | below LOD. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva intestinalis2014–2019 | range. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva lactuca2014–2019 | below LOD. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedDuinker et al. 2020 | Ulva lactuca2014–2019 | range. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Green algae2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Green algae2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Sea lettuce / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedEFSA 2023 seaweed report | Sea lettuce / Fresh product2011–2022Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro2019–2020Wet (fresh) weight | range. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro, Ovar, Su2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro, Torreira, Au2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro, Torreira, Su2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Ria Formosa, Aeroporto de Faro, Sp2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Ria Formosa2019–2020Wet (fresh) weight | range. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Ria Formosa, Faro, Sp2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Ria Formosa, Tavira, Au2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Ria Formosa, Tavira, Sp2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Ria Formosa, Tavira, Su2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary2019–2020Wet (fresh) weight | range. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Samouco, Au2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Samouco, Sp2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Samouco, Su2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Samouco, Wi2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Seixal, Au2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Seixal, Sp2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Seixal, Su2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Seixal, Wi2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Trancao, Au2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Trancao, Sp2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Trancao, Su2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Trancao, Wi2019–2020Wet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedSundhar et al. 2023 | C. racemosa RawCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedSundhar et al. 2023 | U. lactuca RawCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedUnknown 2025 | Caulerpa racemosa, Providence2024Wet (fresh) weight | sample value. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Alaria esculenta2014–2019 | below LOD. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Alaria esculenta2014–2019 | range. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Chorda filum2014–2019 | below LOD. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Chorda filum2014–2019 | below LOD. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Halidrys siliquosa2014–2019 | range. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Sargassum muticum2014–2019 | below LOD. | ||
| Other brown · fresh or wild-collectedDuinker et al. 2020 | Sargassum muticum2014–2019 | below LOD. | ||
| Other brown · fresh or wild-collectedEFSA 2023 seaweed report | pooled fresh/unprocessed brown2011–2022Wet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedEFSA 2023 seaweed report | pooled fresh/unprocessed brown2011–2022Wet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | mean.Same samples: up to 250 µg/kg (range maximum) | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | median. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | range. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other red · fresh or wild-collectedDuinker et al. 2020 | Vertebrata lanosa2014–2019 | below LOD. | ||
| Other red · fresh or wild-collectedDuinker et al. 2020 | Vertebrata lanosa2014–2019 | range. | ||
| Other red · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro2019–2020Wet (fresh) weight | range. | ||
| Other red · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro2019–2020Wet (fresh) weight | mean. | ||
| Other red · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro2019–2020Wet (fresh) weight | mean. | ||
| Other red · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro, Ovar, Su2019–2020Wet (fresh) weight | mean. | ||
| Other red · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro, Torreira, Au2019–2020Wet (fresh) weight | mean. | ||
| Other red · fresh or wild-collectedCardoso et al. 2023 | Ria de Aveiro, Torreira, Su2019–2020Wet (fresh) weight | mean. | ||
| Other red · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary2019–2020Wet (fresh) weight | range. | ||
| Other red · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Samouco, Su2019–2020Wet (fresh) weight | mean. | ||
| Other red · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Samouco, Wi2019–2020Wet (fresh) weight | mean. | ||
| Other red · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Seixal, Au2019–2020Wet (fresh) weight | mean. | ||
| Other red · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Seixal, Sp2019–2020Wet (fresh) weight | mean. | ||
| Other red · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Seixal, Su2019–2020Wet (fresh) weight | mean. | ||
| Other red · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Seixal, Wi2019–2020Wet (fresh) weight | mean. | ||
| Other red · fresh or wild-collectedCardoso et al. 2023 | Tagus estuary, Trancao, Su2019–2020Wet (fresh) weight | mean. | ||
| Other red · fresh or wild-collectedSundhar et al. 2023 | K. aliverzii RawCollection date unreportedWet (fresh) weight | mean. | ||
| Other red · fresh or wild-collectedUnknown 2025 | Asparagopsis taxiformis2024Wet (fresh) weight | sample value. | ||
| Other red · fresh or wild-collectedUnknown 2025 | Gracilaria salicornia, Port Glaud2024Wet (fresh) weight | sample value. | ||
| Other red · fresh or wild-collectedUnknown 2025 | Gracilaria salicornia, Port Glaud2024Wet (fresh) weight | sample value. | ||
| Mixed or unspecified · fresh or wild-collectedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Wet (fresh) weight | mean. | ||
| Mixed or unspecified · fresh or wild-collectedEFSA 2023 seaweed report | Algae and prokaryotes organisms2011–2022Wet (fresh) weight | mean. | ||
| Mixed or unspecified · fresh or wild-collectedUnknown 2025 | all seaweed species and sites2024Wet (fresh) weight | mean. | ||
| Mixed or unspecified · fresh or wild-collectedUnknown 2025 | polluted sites2024Wet (fresh) weight | mean. | ||
| Mixed or unspecified · fresh or wild-collectedUnknown 2025 | Providence site2024Wet (fresh) weight | median. | ||
| Mixed or unspecified · fresh or wild-collectedUnknown 2025 | unpolluted sites2024Wet (fresh) weight | mean. | ||
9 findings · 3 studies | ||||
| Kombu/kelp · form not statedZhao et al. 2016 | Laminaria japonicaCollection date unreportedWet (fresh) weight | range. | ||
| Nori/laver · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Nori/laver · form not statedZhao et al. 2016 | Porphyra teneraCollection date unreported | range. | ||
| Dulse · form not statedEFSA 2023 seaweed report | Dulse / Unspecified2011–2022Basis not stated | mean. | ||
| Dulse · form not statedEFSA 2023 seaweed report | Dulse / Unspecified2011–2022Basis not stated | mean. | ||
| Green seaweeds (Ulva etc.) · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Other brown · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Other red · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Mixed or unspecified · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
1 finding · 1 study | ||||
| Nori/laver · roasted or seasonedAlmela et al. 2002 | retail product 5Collection date unreported | sample value. | ||
13 findings · 2 studies | ||||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa BoiledCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa MWCCollection date unreportedWet (fresh) weight | not detected. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa SCTCollection date unreportedWet (fresh) weight | not detected. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca BoiledCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca MWCCollection date unreportedWet (fresh) weight | not detected. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca SCTCollection date unreportedWet (fresh) weight | not detected. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii BoiledCollection date unreportedWet (fresh) weight | not detected. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii MWCCollection date unreportedWet (fresh) weight | not detected. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii SCTCollection date unreportedWet (fresh) weight | not detected. | ||
| Mixed or unspecified · cookedLin et al. 2021 | AlgaeCollection date unreportedBasis not stated | mean. | ||
| Mixed or unspecified · cookedLin et al. 2021 | AlgaeCollection date unreportedBasis not stated | mean. | ||
| Mixed or unspecified · cookedLin et al. 2021 | AlgaeCollection date unreportedBasis not stated | not detected. | ||
| Mixed or unspecified · cookedLin et al. 2021 | AlgaeCollection date unreportedBasis not stated | range. | ||
3 findings · 1 study | ||||
| Mixed or unspecified · salted, seasoned or preparedKim et al. 2023 | Sea algae2021Basis not stated | mean. | ||
| Mixed or unspecified · salted, seasoned or preparedKim et al. 2023 | Sea algae2021Basis not stated | not detected. | ||
| Mixed or unspecified · salted, seasoned or preparedKim et al. 2023 | Sea algae2021Basis not stated | max. | ||
5 findings · 1 study | ||||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHarding et al. 2018 | Bladder wrack2003Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHarding et al. 2018 | Bladder wrack2003Wet (fresh) weight | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHarding et al. 2018 | Knotted wrack2003Wet (fresh) weight | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHarding et al. 2018 | Knotted wrack2003Wet (fresh) weight | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHarding et al. 2018 | Knotted wrack2003Wet (fresh) weight | range. | ||
1 finding · 1 study | ||||
| Mixed or unspecified · salted, seasoned or preparedKim et al. 2023 | Sea algae2021Basis not stated | not detected. | ||
139 findings · 7 studies · 5 spread figures folded in | ||||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-1Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-2Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-3Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-4Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | RMJKCollection date unreported | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample I: White Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample II: White Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample III: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample IV: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample V: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample VI: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 12023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 22023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 32023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | WWT2023 | mean. | ||
| Green seaweeds (Ulva etc.) · driedAykut et al. 2018 | Kadın Creek2011–2012 | mean.Same samples: 1,020–16,800 µg/kg (range) | ||
| Green seaweeds (Ulva etc.) · driedAykut et al. 2018 | Kadın Creek2011–2012 | range. | ||
| Other brown · driedRodríguez-Rodríguez et al. 2026 | Raw Sargassum composite2024Basis not stated | sample value. | ||
| Other red · driedKhandaker et al. 2021 | all Malaysian samples2018 | mean. | ||
| Other red · driedKhandaker et al. 2021 | Kota Belud farm2018 | mean.Same samples: 6,900–14,300 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Kota Belud farm2018 | range. | ||
| Other red · driedKhandaker et al. 2021 | Langkawi farm2018 | mean.Same samples: 12,300–13,400 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Langkawi farm2018 | range. | ||
| Other red · driedKhandaker et al. 2021 | Semporna farm2018 | mean.Same samples: 8,000–12,800 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Semporna farm2018 | range. | ||
| Mixed or unspecified · driedOwnsworth et al. 2019 | all Scottish macroalgae studiedCollection date unreported | mean.Same samples: 160–3,100 µg/kg (range) | ||
| Mixed or unspecified · driedOwnsworth et al. 2019 | all Scottish macroalgae studiedCollection date unreported | range. | ||
95 findings · 3 studies · 2 spread figures folded in | ||||
| Kombu/kelp · fresh or wild-collectedSund et al. 2026 | Unprocessed2023 | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | mean.Same samples: up to 11,600 µg/kg (range maximum) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | mean.Same samples: 4,210–7,080 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | sample value. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedSundhar et al. 2023 | C. racemosa RawCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedSundhar et al. 2023 | U. lactuca RawCollection date unreportedWet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other red · fresh or wild-collectedSundhar et al. 2023 | K. aliverzii RawCollection date unreportedWet (fresh) weight | mean. | ||
6 findings · 1 study | ||||
| Green seaweeds (Ulva etc.) · powderNour et al. 2025 | Ulva clathrata2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Padina pavonica2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Sargassum ilicifolium2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Sargassum latifolium2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Turbinaria decurrens2021 | mean. | ||
| Other red · powderNour et al. 2025 | Hypnea musciformis2021 | mean. | ||
9 findings · 1 study | ||||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa BoiledCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa MWCCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa SCTCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca BoiledCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca MWCCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca SCTCollection date unreportedWet (fresh) weight | mean. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii BoiledCollection date unreportedWet (fresh) weight | not detected. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii MWCCollection date unreportedWet (fresh) weight | mean. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii SCTCollection date unreportedWet (fresh) weight | not detected. | ||
157 findings · 9 studies · 4 spread figures folded in | ||||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Atlantic Road2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Bakers Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Brace Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Eagle Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Gallops Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Great Pigs Rock2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Misery Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Norman's Woe2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Northern Farmed site2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Rams Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Southern Farmed sites2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShaughnessy et al. 2023 | Tinker's Island2018–2021 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample I: White Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample II: White Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample III: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample IV: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample V: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample VI: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 12023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 22023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | PEF 32023 | mean. | ||
| Kombu/kelp · driedSund et al. 2026 | WWT2023 | mean. | ||
| Dulse · driedBehnaz et al. 2016 | Palmaria palmata, Fornæs, Denmark2011 | mean. | ||
| Carrageen (Irish moss) · driedBehnaz et al. 2016 | Chondrus crispus, Fornæs, Denmark2011 | mean. | ||
| Green seaweeds (Ulva etc.) · driedAykut et al. 2018 | Kadın Creek2011–2012 | mean.Same samples: 190–22,700 µg/kg (range) | ||
| Green seaweeds (Ulva etc.) · driedAykut et al. 2018 | Kadın Creek2011–2012 | range. | ||
| Green seaweeds (Ulva etc.) · driedRakib et al. 2021 | Chlorophyta2018–2019 | mean. | ||
| Green seaweeds (Ulva etc.) · driedRakib et al. 2021 | G10 Ulva compressa2018–2019 | mean. | ||
| Green seaweeds (Ulva etc.) · driedRakib et al. 2021 | G8 Caulerpa racemosa2018–2019 | mean. | ||
| Green seaweeds (Ulva etc.) · driedRakib et al. 2021 | G9 Enteromorpha intestinalis2018–2019 | mean. | ||
| Other brown · driedRakib et al. 2021 | B5 Padina tetrastromatica2018–2019 | mean. | ||
| Other brown · driedRakib et al. 2021 | B6 Sargassum oligocystum2018–2019 | mean. | ||
| Other brown · driedRakib et al. 2021 | B7 Padina boryana2018–2019 | mean. | ||
| Other brown · driedRakib et al. 2021 | Phaeophyta2018–2019 | mean. | ||
| Other brown · driedRodríguez-Rodríguez et al. 2026 | Raw Sargassum composite2024Basis not stated | sample value. | ||
| Other red · driedAziz et al. 2021 | G. tenuistipitata var. liuiCollection date unreported | sample value. | ||
| Other red · driedBehnaz et al. 2016 | Ahnfeltia plicata, Fornæs, Denmark2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Delesseria sanguinea2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Dilsea carnosa, Fornæs, Denmark2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Furcellaria lumbricalis2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Gracilaria vermiculophylla2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Odonthalia dentata2011 | mean. | ||
| Other red · driedBehnaz et al. 2016 | Phycodrys rubens, Fornæs, Denmark2011 | mean. | ||
| Other red · driedKhandaker et al. 2021 | all Malaysian samples2018 | mean. | ||
| Other red · driedKhandaker et al. 2021 | Kota Belud farm2018 | mean.Same samples: 32,900–47,400 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Kota Belud farm2018 | range. | ||
| Other red · driedKhandaker et al. 2021 | Langkawi farm2018 | mean.Same samples: 37,000–45,800 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Langkawi farm2018 | range. | ||
| Other red · driedKhandaker et al. 2021 | Semporna farm2018 | mean.Same samples: 23,800–36,800 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Semporna farm2018 | range. | ||
| Other red · driedRakib et al. 2021 | R1 Hypnea musciformis2018–2019 | mean. | ||
| Other red · driedRakib et al. 2021 | R2 Hypnea pannosa2018–2019 | mean. | ||
| Other red · driedRakib et al. 2021 | R3 Jania rubens2018–2019 | mean. | ||
| Other red · driedRakib et al. 2021 | R4 Gelidium pusillum2018–2019 | mean. | ||
| Other red · driedRakib et al. 2021 | Rhodophyta2018–2019 | mean. | ||
| Mixed or unspecified · driedRakib et al. 2021 | mean of 10 species2018–2019 | mean. | ||
97 findings · 4 studies · 3 spread figures folded in | ||||
| Kombu/kelp · fresh or wild-collectedSund et al. 2026 | Unprocessed2023 | mean. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | mean.Same samples: up to 5,120 µg/kg (range maximum) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015 | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus distichus2015Wet (fresh) weight | below LOD. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | mean.Same samples: 220–5,490 µg/kg (range) | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | median. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | range. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015 | sample value. | ||
| Wracks (Fucus/Ascophyllum) · fresh or wild-collectedHahn et al. 2022 | Fucus spiralis2015Wet (fresh) weight | sample value. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedSundhar et al. 2023 | C. racemosa RawCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · fresh or wild-collectedSundhar et al. 2023 | U. lactuca RawCollection date unreportedWet (fresh) weight | mean. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | mean.Same samples: up to 430 µg/kg (range maximum) | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | median. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | range. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | below LOD. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other brown · fresh or wild-collectedHahn et al. 2022 | Nereocystis luetkeana2015 | sample value. | ||
| Other red · fresh or wild-collectedSundhar et al. 2023 | K. aliverzii RawCollection date unreportedWet (fresh) weight | mean. | ||
| Mixed or unspecified · fresh or wild-collectedRakib et al. 2021 | mean of 10 species2018–2019Wet (fresh) weight | mean. | ||
2 findings · 1 study | ||||
| Kombu/kelp · form not statedZhao et al. 2016 | Laminaria japonicaCollection date unreportedWet (fresh) weight | range. | ||
| Nori/laver · form not statedZhao et al. 2016 | Porphyra teneraCollection date unreported | range. | ||
6 findings · 1 study | ||||
| Green seaweeds (Ulva etc.) · powderNour et al. 2025 | Ulva clathrata2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Padina pavonica2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Sargassum ilicifolium2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Sargassum latifolium2021 | mean. | ||
| Other brown · powderNour et al. 2025 | Turbinaria decurrens2021 | mean. | ||
| Other red · powderNour et al. 2025 | Hypnea musciformis2021 | mean. | ||
9 findings · 1 study | ||||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa BoiledCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa MWCCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | C. racemosa SCTCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca BoiledCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca MWCCollection date unreportedWet (fresh) weight | mean. | ||
| Green seaweeds (Ulva etc.) · cookedSundhar et al. 2023 | U. lactuca SCTCollection date unreportedWet (fresh) weight | mean. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii BoiledCollection date unreportedWet (fresh) weight | not detected. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii MWCCollection date unreportedWet (fresh) weight | mean. | ||
| Other red · cookedSundhar et al. 2023 | K. aliverzii SCTCollection date unreportedWet (fresh) weight | mean. | ||
16 findings · 5 studies · 4 spread figures folded in | ||||
| Hijiki · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Kombu/kelp · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample I: White Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample II: White Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample III: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample IV: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample V: Yellow Sea2014–2016 | sample value. | ||
| Kombu/kelp · driedShchukin et al. 2018 | sample VI: Yellow Sea2014–2016 | sample value. | ||
| Wakame · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Nori/laver · driedWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Green seaweeds (Ulva etc.) · driedAykut et al. 2018 | Kadın Creek2011–2012 | mean.Same samples: 127,000–766,000 µg/kg (range) | ||
| Green seaweeds (Ulva etc.) · driedAykut et al. 2018 | Kadın Creek2011–2012 | range. | ||
| Other brown · driedRodríguez-Rodríguez et al. 2026 | Raw Sargassum composite2024Basis not stated | sample value. | ||
| Other red · driedKhandaker et al. 2021 | all Malaysian samples2018 | mean. | ||
| Other red · driedKhandaker et al. 2021 | Kota Belud farm2018 | mean.Same samples: 32,400–39,600 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Kota Belud farm2018 | range. | ||
| Other red · driedKhandaker et al. 2021 | Langkawi farm2018 | mean.Same samples: 47,600–98,600 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Langkawi farm2018 | range. | ||
| Other red · driedKhandaker et al. 2021 | Semporna farm2018 | mean.Same samples: 16,700–20,400 µg/kg (range) | ||
| Other red · driedKhandaker et al. 2021 | Semporna farm2018 | range. | ||
2 findings · 1 study | ||||
| Kombu/kelp · powder or flakesWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
| Wakame · powder or flakesWHO GEMS/Food | WHO region WPRO; random sampling2024Dried product as sold | median. | ||
3 findings · 1 study | ||||
| Kombu/kelp · cookedWang et al. 2020 | Jilin ProvinceCollection date unreportedAs prepared (soaked or cooked) | mean. | ||
| Kombu/kelp · cookedWang et al. 2020 | Other AreaCollection date unreportedAs prepared (soaked or cooked) | mean. | ||
| Kombu/kelp · cookedWang et al. 2020 | Songhua River AreaCollection date unreportedAs prepared (soaked or cooked) | mean. | ||
5 findings · 1 study | ||||
| Nori/laver · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Green seaweeds (Ulva etc.) · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Other brown · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Other red · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
| Mixed or unspecified · form not statedWHO GEMS/Food | WHO region WPRO; random sampling2024As sold, moisture not stated | median. | ||
6 findings · 1 study · 1 spread figure folded in | ||||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-1Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-2Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-3Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | HOK-4Collection date unreported | sample value. | ||
| Kombu/kelp · driedOwnsworth et al. 2019 | RMJKCollection date unreported | sample value. | ||
| Mixed or unspecified · driedOwnsworth et al. 2019 | all Scottish macroalgae studiedCollection date unreported | mean.Same samples: 97–810 µg/kg (range) | ||
| Mixed or unspecified · driedOwnsworth et al. 2019 | all Scottish macroalgae studiedCollection date unreported | 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 seaweed iAs reference (dried product as sold) · 5 sampling families
Reference and scope
HMI seaweed iAs reference (dried product as sold) · 5 sampling families. Dried product as sold, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤50 | 100–200 (bounded) | 2400 |
| Alternative weighting | ≤50 | 90–290 (bounded) | 2400 |
142 reference units; 5 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 81 | 20% |
| FSANZ 2010 seaweed survey | 18 | 20% |
| McSheehy et al. 2000 | 10 | 20% |
| Rose et al. 2007 | 31 | 20% |
| Matsumoto-Tanibuchi et al. 2019 | 2 | 20% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (dried product as sold): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
- WHO GEMS/Food
- FSANZ 2010 seaweed survey
- McSheehy et al. 2000
- Rose et al. 2007
- Matsumoto-Tanibuchi et al. 2019
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-iAs-dried-product-as-sold:3cd5a62169c9
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed iAs reference (dry weight) · 10 sampling families
Reference and scope
HMI seaweed iAs reference (dry weight) · 10 sampling families. Dry weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 100 | 300 | 24000 |
| Alternative weighting | 100 | 300 | 24000 |
186 reference units; 10 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 10% |
| Duinker et al. 2020 | 27 | 10% |
| Almela et al. 2002 | 18 | 10% |
| García-Salgado et al. 2012 | 10 | 10% |
| Laparra et al. 2003 | 5 | 10% |
| Shimoda et al. 2010 | 9 | 10% |
| Llorente-Mirandes et al. 2011 | 6 | 10% |
| Ownsworth et al. 2019 | 1 | 10% |
| Shaughnessy et al. 2023 | 105 | 10% |
| Ronan et al. 2017 | 2 | 10% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (dry weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
- WHO GEMS/Food
- Duinker et al. 2020
- Almela et al. 2002
- García-Salgado et al. 2012
- Laparra et al. 2003
- Shimoda et al. 2010
- Llorente-Mirandes et al. 2011
- Ownsworth et al. 2019
- Shaughnessy et al. 2023
- Ronan et al. 2017
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-iAs-dry-weight:4e2abe137da9
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed iAs reference (as prepared (soaked or cooked)) · 2 sampling families
Reference and scope
HMI seaweed iAs reference (as prepared (soaked or cooked)) · 2 sampling families. As prepared (soaked or cooked), µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤300 | 13000 | 13000 |
| Alternative weighting | ≤300 | 13000 | 13000 |
25 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Ichikawa et al. 2010 | 1 | 50% |
| Rose et al. 2007 | 24 | 50% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (as prepared (soaked or cooked)): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-iAs-as-prepared:d63f1278cfd0
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed iAs reference (wet product as sold or prepared) · 1 sampling families
Reference and scope
HMI seaweed iAs reference (wet product as sold or prepared) · 1 sampling families. Wet product as sold or prepared, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤26 | 20–50 (bounded) | 100–115 (bounded) |
| Alternative weighting | ≤26 | 20–50 (bounded) | 100–115 (bounded) |
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 from every compatible seaweed sampling family in the evidence ledger on one basis (wet product as sold or prepared): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-iAs-wet-product-as-sold-or-prepared:0a5daff54034
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed tAs reference (dried product as sold) · 4 sampling families
Reference and scope
HMI seaweed tAs reference (dried product as sold) · 4 sampling families. Dried product as sold, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 18600 | 30400 | 54000 |
| Alternative weighting | 18600 | 30100 | 50900 |
111 reference units; 4 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 58 | 25% |
| McSheehy et al. 2000 | 10 | 25% |
| Rose et al. 2007 | 31 | 25% |
| Nischwitz et al. 2006 | 12 | 25% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (dried product as sold): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-tAs-dried-product-as-sold:bbc55cc49da7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed tAs reference (dry weight) · 17 sampling families
Reference and scope
HMI seaweed tAs reference (dry weight) · 17 sampling families. Dry weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 24000 | 40700 | 64400 |
| Alternative weighting | 24000 | 40700 | 64400 |
345 reference units; 17 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 4 | 6% |
| Almela et al. 2002 | 18 | 6% |
| García-Salgado et al. 2012 | 12 | 6% |
| García-Salgado et al. 2012 | 2 | 6% |
| Ichikawa et al. 2006 | 18 | 6% |
| Laparra et al. 2003 | 5 | 6% |
| Shimoda et al. 2010 | 9 | 6% |
| Zhao et al. 2014 | 5 | 6% |
| Llorente-Mirandes et al. 2011 | 6 | 6% |
| Shaughnessy et al. 2023 | 117 | 6% |
| Shchukin et al. 2018 | 6 | 6% |
| Tukai et al. 2002 | 13 | 6% |
| Morita et al. 1990 | 38 | 6% |
| Hahn et al. 2022 | 64 | 6% |
| Ronan et al. 2017 | 2 | 6% |
| Nepper-Davidsen et al. 2023 | 24 | 6% |
| Petursdottir 2015 | 2 | 6% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (dry weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
- WHO GEMS/Food
- Almela et al. 2002
- García-Salgado et al. 2012
- García-Salgado et al. 2012
- Ichikawa et al. 2006
- Laparra et al. 2003
- Shimoda et al. 2010
- Zhao et al. 2014
- Llorente-Mirandes et al. 2011
- Shaughnessy et al. 2023
- Shchukin et al. 2018
- Tukai et al. 2002
- Morita et al. 1990
- Hahn et al. 2022
- Ronan et al. 2017
- Nepper-Davidsen et al. 2023
- Petursdottir 2015
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-tAs-dry-weight:485537c8468f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed tAs reference (as prepared (soaked or cooked)) · 2 sampling families
Reference and scope
HMI seaweed tAs reference (as prepared (soaked or cooked)) · 2 sampling families. As prepared (soaked or cooked), µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 5500 | 28000 | 28000 |
| Alternative weighting | 4600 | 28000 | 28000 |
25 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Ichikawa et al. 2010 | 1 | 50% |
| Rose et al. 2007 | 24 | 50% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (as prepared (soaked or cooked)): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-tAs-as-prepared:220008110714
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed tAs reference (wet product as sold or prepared) · 1 sampling families
Reference and scope
HMI seaweed tAs reference (wet product as sold or prepared) · 1 sampling families. Wet product as sold or prepared, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2500 | 7500 | 17000 |
| Alternative weighting | 2500 | 7500 | 17000 |
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 from every compatible seaweed sampling family in the evidence ledger on one basis (wet product as sold or prepared): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-tAs-wet-product-as-sold-or-prepared:ab59b68df364
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed tAs reference (wet (fresh) weight) · 2 sampling families
Reference and scope
HMI seaweed tAs reference (wet (fresh) weight) · 2 sampling families. Wet (fresh) weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2280 | 3640 | 5790 |
| Alternative weighting | 2280 | 3640 | 5790 |
29 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Morita et al. 1990 | 4 | 50% |
| Hahn et al. 2022 | 25 | 50% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (wet (fresh) weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-tAs-wet-weight:5cfbf4952c7d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed DMA reference (dry weight) · 6 sampling families
Reference and scope
HMI seaweed DMA reference (dry weight) · 6 sampling families. Dry weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 200 | 550 | 1300 |
| Alternative weighting | 200 | 550 | 1300 |
42 reference units; 6 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 3 | 17% |
| García-Salgado et al. 2012 | 7 | 17% |
| Ichikawa et al. 2006 | 12 | 17% |
| Shimoda et al. 2010 | 9 | 17% |
| Zhao et al. 2014 | 5 | 17% |
| Llorente-Mirandes et al. 2011 | 6 | 17% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (dry weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
- WHO GEMS/Food
- García-Salgado et al. 2012
- Ichikawa et al. 2006
- Shimoda et al. 2010
- Zhao et al. 2014
- Llorente-Mirandes et al. 2011
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-DMA-dry-weight:b7a7ec010ffb
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed DMA reference (dried product as sold) · 2 sampling families
Reference and scope
HMI seaweed DMA reference (dried product as sold) · 2 sampling families. Dried product as sold, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 300 | 2980 | 5350 |
| Alternative weighting | 300 | 2980 | 5350 |
13 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 50% |
| Nischwitz et al. 2006 | 12 | 50% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (dried product as sold): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-DMA-dried-product-as-sold:5032729ee7b5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed Cd reference (dried product as sold) · 1 sampling families
Reference and scope
HMI seaweed Cd reference (dried product as sold) · 1 sampling families. Dried product as sold, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 160 | 540 | 1750 |
| Alternative weighting | 160 | 540 | 1750 |
23 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 23 | 100% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (dried product as sold): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-Cd-dried-product-as-sold:b7ef3ba22e0d
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed Cd reference (dry weight) · 8 sampling families
Reference and scope
HMI seaweed Cd reference (dry weight) · 8 sampling families. Dry weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 180 | 550 | 1480 |
| Alternative weighting | 180 | 550 | 1480 |
261 reference units; 8 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Duinker et al. 2020 | 27 | 12% |
| Almela et al. 2002 | 18 | 13% |
| Ownsworth et al. 2019 | 4 | 13% |
| Shaughnessy et al. 2023 | 117 | 12% |
| Shchukin et al. 2018 | 6 | 12% |
| Hahn et al. 2022 | 64 | 13% |
| Nepper-Davidsen et al. 2023 | 24 | 12% |
| Aziz et al. 2021 | 1 | 13% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (dry weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
- Duinker et al. 2020
- Almela et al. 2002
- Ownsworth et al. 2019
- Shaughnessy et al. 2023
- Shchukin et al. 2018
- Hahn et al. 2022
- Nepper-Davidsen et al. 2023
- Aziz et al. 2021
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-Cd-dry-weight:5f20697db670
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed Cd reference (wet (fresh) weight) · 2 sampling families
Reference and scope
HMI seaweed Cd reference (wet (fresh) weight) · 2 sampling families. Wet (fresh) weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 418 | 1230 | 1600 |
| Alternative weighting | 418 | 1230 | 1600 |
26 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Hahn et al. 2022 | 25 | 50% |
| Groleau et al. 2025 | 1 | 50% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (wet (fresh) weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-Cd-wet-weight:8d5b383a48e7
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed Cd reference (wet product as sold or prepared) · 1 sampling families
Reference and scope
HMI seaweed Cd reference (wet product as sold or prepared) · 1 sampling families. Wet product as sold or prepared, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 710 | 710 | 710 |
| Alternative weighting | 710 | 710 | 710 |
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 from every compatible seaweed sampling family in the evidence ledger on one basis (wet product as sold or prepared): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-Cd-wet-product-as-sold-or-prepared:ebf3e65ad558
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed Pb reference (dried product as sold) · 2 sampling families
Reference and scope
HMI seaweed Pb reference (dried product as sold) · 2 sampling families. Dried product as sold, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 193 | 340 | 340 |
| Alternative weighting | 193 | 340 | 340 |
43 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 42 | 50% |
| Wang et al. 2019 | 1 | 50% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (dried product as sold): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-Pb-dried-product-as-sold:e8bdf7df22d5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed Pb reference (dry weight) · 9 sampling families
Reference and scope
HMI seaweed Pb reference (dry weight) · 9 sampling families. Dry weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 31–100 (bounded) | 200 | 530 |
| Alternative weighting | 31–100 (bounded) | 200 | 530 |
263 reference units; 9 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 12 | 11% |
| Duinker et al. 2020 | 25 | 11% |
| Almela et al. 2002 | 13 | 11% |
| Ownsworth et al. 2019 | 5 | 11% |
| Shaughnessy et al. 2023 | 117 | 11% |
| Shchukin et al. 2018 | 6 | 11% |
| Hahn et al. 2022 | 62 | 11% |
| Nepper-Davidsen et al. 2023 | 22 | 11% |
| Aziz et al. 2021 | 1 | 11% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (dry weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
- WHO GEMS/Food
- Duinker et al. 2020
- Almela et al. 2002
- Ownsworth et al. 2019
- Shaughnessy et al. 2023
- Shchukin et al. 2018
- Hahn et al. 2022
- Nepper-Davidsen et al. 2023
- Aziz et al. 2021
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-Pb-dry-weight:8c889ebc5ec8
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed Pb reference (wet product as sold or prepared) · 1 sampling families
Reference and scope
HMI seaweed Pb reference (wet product as sold or prepared) · 1 sampling families. Wet product as sold or prepared, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤90 | 60–97.5 (bounded) | 115 |
| Alternative weighting | ≤90 | 60–97.5 (bounded) | 115 |
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 from every compatible seaweed sampling family in the evidence ledger on one basis (wet product as sold or prepared): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-Pb-wet-product-as-sold-or-prepared:26fc9d26ffaa
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed Pb reference (wet (fresh) weight) · 2 sampling families
Reference and scope
HMI seaweed Pb reference (wet (fresh) weight) · 2 sampling families. Wet (fresh) weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤24 | 570 | 570 |
| Alternative weighting | ≤24 | 570 | 570 |
26 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Hahn et al. 2022 | 25 | 50% |
| Groleau et al. 2025 | 1 | 50% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (wet (fresh) weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-Pb-wet-weight:e037c87eb888
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed tHg reference (dried product as sold) · 1 sampling families
Reference and scope
HMI seaweed tHg reference (dried product as sold) · 1 sampling families. Dried product as sold, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | ≤50 | 10–50 (bounded) |
| Alternative weighting | ≤10 | ≤50 | 10–50 (bounded) |
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 from every compatible seaweed sampling family in the evidence ledger on one basis (dried product as sold): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-tHg-dried-product-as-sold:97d063ad7d8f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed tHg reference (dry weight) · 6 sampling families
Reference and scope
HMI seaweed tHg reference (dry weight) · 6 sampling families. Dry weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤10 | 11.3–24.8 (bounded) | 30–53 (bounded) |
| Alternative weighting | ≤10 | 11.3–24.8 (bounded) | 30–53 (bounded) |
233 reference units; 6 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Duinker et al. 2020 | 8 | 17% |
| Almela et al. 2002 | 18 | 17% |
| Shaughnessy et al. 2023 | 117 | 17% |
| Shchukin et al. 2018 | 6 | 17% |
| Hahn et al. 2022 | 62 | 17% |
| Nepper-Davidsen et al. 2023 | 22 | 17% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (dry weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
- Duinker et al. 2020
- Almela et al. 2002
- Shaughnessy et al. 2023
- Shchukin et al. 2018
- Hahn et al. 2022
- Nepper-Davidsen et al. 2023
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-tHg-dry-weight:11887b9feed1
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed tHg reference (wet (fresh) weight) · 3 sampling families
Reference and scope
HMI seaweed tHg reference (wet (fresh) weight) · 3 sampling families. Wet (fresh) weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤3.8 | 3.8–8.6 (bounded) | 6.2–16 (bounded) |
| Alternative weighting | ≤4.65 | 3.8–8.6 (bounded) | 6.2–16 (bounded) |
32 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Hahn et al. 2022 | 25 | 33% |
| Harding et al. 2018 | 2 | 33% |
| Unknown 2025 | 5 | 33% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (wet (fresh) weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-tHg-wet-weight:f53878c4d800
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed Ni reference (dry weight) · 4 sampling families
Reference and scope
HMI seaweed Ni reference (dry weight) · 4 sampling families. Dry weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 140 | 322 | 1500 |
| Alternative weighting | 140 | 322 | 1500 |
190 reference units; 4 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Ownsworth et al. 2019 | 4 | 25% |
| Shaughnessy et al. 2023 | 117 | 25% |
| Shchukin et al. 2018 | 6 | 25% |
| Hahn et al. 2022 | 63 | 25% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (dry weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-Ni-dry-weight:38813342509e
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed Ni reference (wet (fresh) weight) · 1 sampling families
Reference and scope
HMI seaweed Ni reference (wet (fresh) weight) · 1 sampling families. Wet (fresh) weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 49.5 | 224 | 786 |
| Alternative weighting | 49.5 | 224 | 786 |
25 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Hahn et al. 2022 | 25 | 100% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (wet (fresh) weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-Ni-wet-weight:cc90aad1433a
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed Cr reference (dry weight) · 4 sampling families
Reference and scope
HMI seaweed Cr reference (dry weight) · 4 sampling families. Dry weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 60–67.7 (bounded) | 228 | 800 |
| Alternative weighting | 60–67.7 (bounded) | 228 | 800 |
188 reference units; 4 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Shaughnessy et al. 2023 | 117 | 25% |
| Shchukin et al. 2018 | 6 | 25% |
| Hahn et al. 2022 | 64 | 25% |
| Aziz et al. 2021 | 1 | 25% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (dry weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-Cr-dry-weight:681b0131343f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed Cr reference (wet (fresh) weight) · 1 sampling families
Reference and scope
HMI seaweed Cr reference (wet (fresh) weight) · 1 sampling families. Wet (fresh) weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 45.3 | 51 | 105 |
| Alternative weighting | 45.3 | 51 | 105 |
25 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Hahn et al. 2022 | 25 | 100% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (wet (fresh) weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-Cr-wet-weight:026bd667fc8b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed Al reference (dried product as sold) · 1 sampling families
Reference and scope
HMI seaweed Al reference (dried product as sold) · 1 sampling families. Dried product as sold, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 33000 | 41500 | 56000 |
| Alternative weighting | 33000 | 41500 | 56000 |
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 from every compatible seaweed sampling family in the evidence ledger on one basis (dried product as sold): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-Al-dried-product-as-sold:5f019d18114b
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed Al reference (dry weight) · 1 sampling families
Reference and scope
HMI seaweed Al reference (dry weight) · 1 sampling families. Dry weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 71100 | 437000 | 850000 |
| Alternative weighting | 71100 | 437000 | 850000 |
6 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Shchukin et al. 2018 | 6 | 100% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (dry weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-Al-dry-weight:dfb0425f70d5
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI seaweed U reference (dry weight) · 1 sampling families
Reference and scope
HMI seaweed U reference (dry weight) · 1 sampling families. Dry weight, µg/kg; no basis conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 75 | 100 | 170 |
| Alternative weighting | 75 | 100 | 170 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| Ownsworth et al. 2019 | 4 | 100% |
Methods
HMI pools subgroup medians from every compatible seaweed sampling family in the evidence ledger on one basis (dry weight): WHO GEMS/Food medians by seaweed type, product form, WHO region and year (random sampling only), individual sample results printed by surveys, and published subgroup medians. All edible macroalgal types are pooled, so a position shows where a result sits among seaweeds in general; types differ systematically. Each family has equal total weight; subgroups have equal weight within a family. Non-detects stay as zero-to-limit intervals. Means, ranges and maxima never enter as observations.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1–Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
An international evidence-library reference across seaweed types, not a probability sample of any market. Hijiki and some kelps dominate the upper arsenic tail. GEMS/Food regions are reporting regions, not growing origins. Different bases are never mixed. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:seaweed-U-dry-weight:0685a15440a2
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is 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.
Sources and contamination pathways
Seaweeds take up metals directly from seawater across their whole surface, so concentrations reflect the water they grew in, the species and the age of the tissue rather than any soil.4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →21Risks and benefits of consuming edible seaweedsNutrition ReviewsRead source →17Chemical contaminant levels in edible seaweeds of the Salish Sea and implications for their consumptionPLOS ONERead source → Brown seaweeds accumulate arsenic as arsenate because it behaves like phosphate, and laboratory work on hijiki showed arsenate uptake competing with phosphate.22Arsenic contents and speciation at different growth stages of Sargassum fusiforme [Harv.] Setchell (Hijiki), an edible seaweedApplied Ecology and Environmental ResearchRead source →23Arsenic in edible macroalgae: an integrated approachJournal of Toxicology and Environmental Health, Part B: Critical ReviewsRead source → Most of that arsenic is converted to arsenosugars, which is why total arsenic of 20–100 mg/kg dry weight is common in kelp while inorganic arsenic usually stays below 1 mg/kg.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →8Arsenic speciation in edible alga samples by microwave-assisted extraction and high performance liquid chromatography coupled to atomic fluorescence spectrometryAnalytica Chimica ActaRead source →9Concentrations and speciation of arsenic in New England seaweed species harvested for food and agricultureChemosphereRead source →
Hijiki and its Sargassum relatives are the exception because they retain a large inorganic fraction.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source → In Norwegian monitoring, wireweed (Sargassum muticum) had a median of 51 mg/kg inorganic arsenic dry weight and imported hijiki 59 mg/kg, while the other species had medians of 0.23 mg/kg or less except oarweed and sea oak (7.6 mg/kg).4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source → Inorganic arsenic in farmed Chinese hijiki rose through the season, from 40 mg/kg in January to 58 mg/kg dry weight in May.22Arsenic contents and speciation at different growth stages of Sargassum fusiforme [Harv.] Setchell (Hijiki), an edible seaweedApplied Ecology and Environmental ResearchRead source →
Cadmium and lead follow local water and tissue age. In New England sugar kelp, the young base of the blade carried more cadmium and total arsenic than the old tip at every site, while lead and mercury were higher at known contaminated sites.6Evidence of elevated heavy metals concentrations in wild and farmed sugar kelp (Saccharina latissima) in New EnglandScientific ReportsRead source → In the Salish Sea, lead exceeded 9 mg/kg dry weight only at shipyard and harbour sites, and bull kelp at the same sites carried about twice the cadmium of rockweed.17Chemical contaminant levels in edible seaweeds of the Salish Sea and implications for their consumptionPLOS ONERead source →
Variation by seaweed type, origin and preparation
For inorganic arsenic, the lowest observed types on a dried-as-sold basis are nori, wakame, dulse and most kombu.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →3Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaFood Standards Australia New Zealand (FSANZ), Survey reportRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source → Australian retail nori averaged 0.11 mg/kg, wakame 0.18 mg/kg and kombu 0.22 mg/kg, and European dried wakame averaged 0.19 mg/kg and dried laver 0.17 mg/kg.3Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaFood Standards Australia New Zealand (FSANZ), Survey reportRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source → Hijiki is consistently highest in every study that measured it, at 38–96 mg/kg as sold, so avoiding hijiki is a supported sourcing preference rather than a tentative pattern.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →24Determination of Inorganic Arsenic in Seaweed and Seafood by LC-ICP-MS: Method ValidationJournal of AOAC InternationalRead source →25Speciation Analysis of Arsenics in Commercial Hijiki by High Performance Liquid Chromatography-tandem-mass Spectrometry and High Performance Liquid Chromatography-inductively Coupled Plasma Mass SpectrometryJournal of Health Science 56(1):47-56Read source →
Within kelp, species matters more than origin. Oarweed (Laminaria digitata) had 21 mg/kg inorganic arsenic dry weight in Norway, 30–62 mg/kg in Irish blades and 8.3 mg/kg in Maine, while tangle, sugar kelp and Japanese kombu (Saccharina) were at 0.02–0.16 mg/kg in Norway.4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →9Concentrations and speciation of arsenic in New England seaweed species harvested for food and agricultureChemosphereRead source →13High proportions of inorganic arsenic in Laminaria digitata but not in Ascophyllum nodosum samples from IrelandChemosphereRead source → A product sold simply as kelp can therefore differ more than a hundredfold, which is why the species name on the specification matters.4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →13High proportions of inorganic arsenic in Laminaria digitata but not in Ascophyllum nodosum samples from IrelandChemosphereRead source →
Cadmium reverses part of that order. Dried laver had the highest cadmium mean among European seaweed groups (1.68 mg/kg) and dried wakame was next (1.28 mg/kg), while dried kombu averaged 0.46 mg/kg and dulse 0.46 mg/kg.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source → In a Canary Islands market survey, kombu and wakame of declared Galician origin averaged 0.085 and 0.070 mg/kg cadmium dry weight against 0.42 and 0.75 mg/kg for Asian kombu and wakame, about five and eleven times lower, a within-study origin difference that has not been tested elsewhere.18Human Exposure to Toxic Metals (Cd, Pb, Hg) and Nitrates (NO3−) from Seaweed ConsumptionApplied SciencesRead source → These are tentative origin patterns from one study, not a reliable sourcing preference for a country.
Lead and mercury rarely separate the types.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source → Norwegian medians for lead were 0.19–0.93 mg/kg dry weight across common species and mercury medians were 0.005–0.024 mg/kg, and green seaweeds such as gutweed and green sea fingers had the highest lead (0.67–1.4 mg/kg).4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source → Lower inorganic arsenic in nori therefore comes with higher cadmium, and the choice between them depends on which metal matters most for the product.3Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaFood Standards Australia New Zealand (FSANZ), Survey reportRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →
Which seaweeds have the lowest inorganic arsenic?
Nori, wakame, dulse and Saccharina kombu were lowest, at about 0.1–0.3 mg/kg in Australian and European dried products as sold and 0.02–0.16 mg/kg dry weight in Norwegian monitoring.3Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaFood Standards Australia New Zealand (FSANZ), Survey reportRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source → Rockweed (Ascophyllum) was also low, mostly below 0.07 mg/kg dry weight in Irish samples.13High proportions of inorganic arsenic in Laminaria digitata but not in Ascophyllum nodosum samples from IrelandChemosphereRead source → These are the lowest observed types in each study; a single product can still differ, so a result for the lot is the reliable check.
Is all kelp high in arsenic?
No. All kelps carry tens of mg/kg total arsenic, but inorganic arsenic ranges from about 0.02 mg/kg in Norwegian Saccharina kombu to 21 mg/kg in oarweed, and up to 87 mg/kg in decaying Irish oarweed tips.4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →13High proportions of inorganic arsenic in Laminaria digitata but not in Ascophyllum nodosum samples from IrelandChemosphereRead source → The species name, not the word kelp, decides the inorganic arsenic.4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →
Does origin change cadmium in nori and wakame?
Possibly. In one Canary Islands survey, Asian kombu and wakame had about five and eleven times the cadmium of Galician products, and Korean laver from the west coast averaged 0.69 mg/kg against 0.50 mg/kg from the south coast.18Human Exposure to Toxic Metals (Cd, Pb, Hg) and Nitrates (NO3−) from Seaweed ConsumptionApplied SciencesRead source →26Total arsenic, mercury, lead, and cadmium contents in edible dried seaweed in KoreaFood Additives & Contaminants: Part B: SurveillanceRead source → Neither difference has been confirmed by another study.
Processing effects and seaweed derivatives
Soaking and boiling move arsenic out of seaweed into the water, and the water is where it ends up.7Decrease of arsenic in edible brown algae Hijikia fusiforme by the cooking processApplied Organometallic ChemistryRead source →10Estimation of Arsenic Bioaccessibility in Edible Seaweed by an in Vitro Digestion MethodJournal of Agricultural and Food ChemistryRead source →11Tracing the natural and anthropogenic influence on the trace elemental chemistry of estuarine macroalgae and the implications for human consumptionScience of the Total EnvironmentRead source → Japanese-style soaking of dried hijiki eluted 22–32% of total arsenic, and boiling the soaked hijiki eluted a further 53–62%, mostly as arsenate.7Decrease of arsenic in edible brown algae Hijikia fusiforme by the cooking processApplied Organometallic ChemistryRead source → Boiling dried hijiki for 20 minutes lowered inorganic arsenic from 54 to 31 mg/kg dry weight, while baking nori did not change its arsenic.10Estimation of Arsenic Bioaccessibility in Edible Seaweed by an in Vitro Digestion MethodJournal of Agricultural and Food ChemistryRead source →
Commercial processing of hijiki makes a large difference. Open-steamed Japanese hijiki products carried 9–14 mg/kg water-soluble inorganic arsenic dry weight against 51–71 mg/kg for boiled or closed-steam products.25Speciation Analysis of Arsenics in Commercial Hijiki by High Performance Liquid Chromatography-tandem-mass Spectrometry and High Performance Liquid Chromatography-inductively Coupled Plasma Mass SpectrometryJournal of Health Science 56(1):47-56Read source → In Scottish and Japanese kelp, a soup preparation removed 75–96% of inorganic arsenic from the solid seaweed, a 10–20 second blanch 3–61% and a cold soak about 65%.11Tracing the natural and anthropogenic influence on the trace elemental chemistry of estuarine macroalgae and the implications for human consumptionScience of the Total EnvironmentRead source →
Cadmium and lead respond much less. Pulsed electric field and warm-water treatment of Norwegian sugar kelp lowered iodine by up to 25% but did not lower cadmium, mercury or lead on a dry-weight basis; cadmium rose from 0.33 to 0.43 mg/kg after warm water.12Pulsed electric field processing as an alternative to warm water treatment for the reduction of potentially toxic elements in Saccharina latissimaJournal of Applied PhycologyRead source → Boiling Alaria in Nunavik lowered total arsenic but not cadmium, lead or mercury, and the arsenic moved into the broth.27Improving nutritional intakes and reducing metal(loid) exposures from wild fish broth among Inuit pregnant womenScience of the Total EnvironmentRead source →
Does cooking hijiki make it lower in arsenic?
Yes, if the soaking and cooking water is discarded.7Decrease of arsenic in edible brown algae Hijikia fusiforme by the cooking processApplied Organometallic ChemistryRead source →10Estimation of Arsenic Bioaccessibility in Edible Seaweed by an in Vitro Digestion MethodJournal of Agricultural and Food ChemistryRead source → Soaking and boiling together removed most arsenic in Japanese tests, and boiling alone lowered inorganic arsenic from 54 to 31 mg/kg dry weight.7Decrease of arsenic in edible brown algae Hijikia fusiforme by the cooking processApplied Organometallic ChemistryRead source →10Estimation of Arsenic Bioaccessibility in Edible Seaweed by an in Vitro Digestion MethodJournal of Agricultural and Food ChemistryRead source → Prepared hijiki in the UK still averaged 11 mg/kg inorganic arsenic wet weight, far above other prepared seaweeds.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →
Heavy metal mitigation and remediation for seaweed
Controls for seaweed act at four points: species and type choice, growing site and harvest, processing, and household preparation. The best supported are choosing low-arsenic types and kelp species, which changes inorganic arsenic by two orders of magnitude, and soaking then boiling with the water discarded, which removes much of the arsenic that remains.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →7Decrease of arsenic in edible brown algae Hijikia fusiforme by the cooking processApplied Organometallic ChemistryRead source →11Tracing the natural and anthropogenic influence on the trace elemental chemistry of estuarine macroalgae and the implications for human consumptionScience of the Total EnvironmentRead source → Siting and harvest controls are observational: farmed sugar kelp in northern Norway had more than four times the cadmium of southern farms, and using the old blade tip rather than the base lowered cadmium in New England kelp.4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →6Evidence of elevated heavy metals concentrations in wild and farmed sugar kelp (Saccharina latissima) in New EnglandScientific ReportsRead source →
Filter findings
12 control comparisons
About this table
| Control | Material | Effects | Evidence | |||||||||||||||||||||||||||||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Consider farm latitude for cadmium in sugar kelpaquaculture · As reported | Seaweed | Cd · Context | 1Duinker et al. 2020 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators CadmiumHigher cadmium at northern farmsCadmiumNorth versus southDry 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. Northern versus southern Norwegian farms. 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 sugar kelp in the north (68–70°N) had cadmium above 1.0 mg/kg dry weight, more than four times the southern farms; inorganic arsenic showed no such trend.
Design, applicability and operating conditions Observational survey. Siting new kelp farms. One study family. As reported by the source Avoids high-accumulating material, or moves soluble arsenic into water that is discarded. Source measurements and linked outcomes
Observational; site effects confounded with other factors. Percentages as reported or computed from the source table means where stated. Concentrations stay on the source basis; mass yield is not reported unless stated. Trade-offs and implementation Not assessed unless listed in outcomes. Iodine and minerals can fall with arsenic; not quantified unless stated. Soaking and cooking water carries the removed arsenic. Not quantified. Not assessed. Applicability and verification Siting new kelp farms. 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 the older blade tip rather than the base for lower cadmiumharvest and collection · As reported | Seaweed | Cd · Context | 1Shaughnessy et al. 2023 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators CadmiumLower cadmium in blade tipsCadmium exceedance shareBase (80–88%) versus tip (0%)Dry 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. Base versus distal tip of the same blades. 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 The young base of the blade had more cadmium and total arsenic than the distal tip at every site; base cadmium exceeded the EU feed limit in 80–88% of samples, tips in none.
Design, applicability and operating conditions Observational survey. Harvest and trimming of kelp blades. One study family. As reported by the source Avoids high-accumulating material, or moves soluble arsenic into water that is discarded. Source measurements and linked outcomes
Observational; exceedance against a feed limit used by the authors. Percentages as reported or computed from the source table means where stated. Concentrations stay on the source basis; mass yield is not reported unless stated. Trade-offs and implementation Not assessed unless listed in outcomes. Iodine and minerals can fall with arsenic; not quantified unless stated. Soaking and cooking water carries the removed arsenic. Not quantified. Not assessed. Applicability and verification Harvest and trimming of kelp blades. 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. | |||||||||||||||||||||||||||||||||||||||||||||
| Harvest hijiki earlier in the seasonharvest and collection · As reported | Seaweed | iAs · Decreased | 1Huang et al. 2020 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Inorganic arsenicDecreasedLower inorganic arsenic in early-season hijikiInorganic arsenicMay versus January harvestDry weightModerate · HMI calculates the relative change from the retained source means: (40290 − 58000) / 58000 × 100 = -30.5%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Monthly harvests from the same farm. 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 Inorganic arsenic in the native variety rose from 40.3 mg/kg dry weight in January to 58.0 mg/kg in May.
Design, applicability and operating conditions Observational survey. Hijiki farming. One study family. As reported by the source Avoids high-accumulating material, or moves soluble arsenic into water that is discarded. Source measurements and linked outcomes
One farm and season; still far above other seaweeds. Percentages as reported or computed from the source table means where stated. Concentrations stay on the source basis; mass yield is not reported unless stated. Trade-offs and implementation Not assessed unless listed in outcomes. Iodine and minerals can fall with arsenic; not quantified unless stated. Soaking and cooking water carries the removed arsenic. Not quantified. Not assessed. Applicability and verification Hijiki farming. 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 tangle or Saccharina over oarweed kelpsourcing and procurement · As reported | Seaweed | iAs · Decreased | 1Duinker et al. 2020 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Inorganic arsenicDecreasedLower inorganic arsenic in tangle (observational)Median inorganic arsenicOarweed versus tangleDry weightHigh · HMI calculates the relative change from the retained source means: (37 − 21000) / 21000 × 100 = -99.8%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Two kelp species from the same national monitoring programme. 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 Oarweed (Laminaria digitata) had a median of 21 mg/kg inorganic arsenic dry weight (n = 40) against 0.037 mg/kg in tangle (L. hyperborea, n = 4).
Design, applicability and operating conditions Observational survey. Kelp products where the species can be specified. One study family. As reported by the source Avoids high-accumulating material, or moves soluble arsenic into water that is discarded. Source measurements and linked outcomes
Observational; tangle n = 4. Percentages as reported or computed from the source table means where stated. Concentrations stay on the source basis; mass yield is not reported unless stated. Trade-offs and implementation Not assessed unless listed in outcomes. Iodine and minerals can fall with arsenic; not quantified unless stated. Soaking and cooking water carries the removed arsenic. Not quantified. Not assessed. Applicability and verification Kelp products where the species can be specified. 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 hijikisourcing and procurement · As reported | Seaweed | iAs · Decreased | 1Rose et al. 2007 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Inorganic arsenicDecreasedLower inorganic arsenic in other dried seaweedsMean inorganic arsenic as soldHijiki versus kombu (below 0.3 mg/kg)Dried product as soldHigh · HMI calculates the relative change from the retained source means: (300 − 77000) / 77000 × 100 = -99.6%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Hijiki versus other dried seaweeds bought in the same survey. 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 Hijiki averaged 77 mg/kg inorganic arsenic as sold (n = 9); arame, wakame and kombu were below 0.3 mg/kg. UK agencies advised against eating hijiki.
Design, applicability and operating conditions Measured preparation or processing comparison. Any purchasing decision between seaweed types. One study family. As reported by the source Avoids high-accumulating material, or moves soluble arsenic into water that is discarded. Source measurements and linked outcomes
Other types are below the detection limit; their value is an upper bound. Percentages as reported or computed from the source table means where stated. Concentrations stay on the source basis; mass yield is not reported unless stated. Trade-offs and implementation Not assessed unless listed in outcomes. Iodine and minerals can fall with arsenic; not quantified unless stated. Soaking and cooking water carries the removed arsenic. Not quantified. Not assessed. Applicability and verification Any purchasing decision between seaweed types. 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 open-steam processed hijikifood processing · As reported | Seaweed | iAs · Decreased | 1Shimoda et al. 2010 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Inorganic arsenicDecreasedLower water-soluble inorganic arsenic in open-steam productsWater-soluble inorganic arsenicBoiled or closed-steam versus open-steam productsDry weightHigh · HMI calculates the relative change from the retained source means: (13600 − 51100) / 51100 × 100 = -73.4%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Products from different processing systems, not paired lots. 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 Open-steamed products had 9.2–13.6 mg/kg water-soluble inorganic arsenic dry weight against 51–71 mg/kg for boiled or closed-steam products.
Design, applicability and operating conditions Observational survey. Purchasing processed hijiki. One study family. As reported by the source Avoids high-accumulating material, or moves soluble arsenic into water that is discarded. Source measurements and linked outcomes
Not paired lots; water-soluble fraction only. Percentages as reported or computed from the source table means where stated. Concentrations stay on the source basis; mass yield is not reported unless stated. Trade-offs and implementation Not assessed unless listed in outcomes. Iodine and minerals can fall with arsenic; not quantified unless stated. Soaking and cooking water carries the removed arsenic. Not quantified. Not assessed. Applicability and verification Purchasing processed hijiki. 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 blanching-type processing to lower cadmium or leadfood processing · As reported | Seaweed | Cd · Increased Pb · Increased | 1Sund et al. 2026 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators CadmiumIncreasedHigher cadmium after warm-water treatmentCadmiumUnprocessed versus warm-water treatedDry weightModerate · HMI calculates the relative change from the retained source means: (430 − 330) / 330 × 100 = 30.3%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. LeadIncreasedHigher lead after warm-water treatmentLeadUnprocessed versus warm-water treatedDry weightHigh · HMI calculates the relative change from the retained source means: (83 − 54) / 54 × 100 = 53.7%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Unprocessed versus processed portions of one harvest batch. 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 Warm-water treatment and pulsed electric fields lowered iodine by up to 25% but did not lower cadmium, mercury or lead on a dry-weight basis.
Design, applicability and operating conditions Measured preparation or processing comparison. Industrial pre-treatment of kelp. One study family. As reported by the source Avoids high-accumulating material, or moves soluble arsenic into water that is discarded. Source measurements and linked outcomes
One batch, n = 3; dry-weight concentrations rise as soluble matter is lost. Percentages as reported or computed from the source table means where stated. Concentrations stay on the source basis; mass yield is not reported unless stated. Trade-offs and implementation Not assessed unless listed in outcomes. Iodine and minerals can fall with arsenic; not quantified unless stated. Soaking and cooking water carries the removed arsenic. Not quantified. Not assessed. Applicability and verification Industrial pre-treatment of kelp. 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. | |||||||||||||||||||||||||||||||||||||||||||||
| Test imported hijiki for inorganic arsenic at the borderlot acceptance and release · As reported | Seaweed | iAs · Context | GuidanceFSANZ 2010 survey HMI source record · Original source Official guidance; not an independent experimental dataset. Reused across actions without adding studies. Effects and comparators Inorganic arsenicDetection, not removalCompliance share10 of 10 consignments compliantDry 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. Border testing against the Australia and New Zealand limit. 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 All 10 imported hijiki consignments tested from July to December 2010 complied with the 1 mg/kg limit; earlier consignments had failed.
Design, applicability and operating conditions Agency or author guidance. Import control of hijiki. One study family. As reported by the source Avoids high-accumulating material, or moves soluble arsenic into water that is discarded. Source measurements and linked outcomes
Testing detects contamination; it does not lower it. Percentages as reported or computed from the source table means where stated. Concentrations stay on the source basis; mass yield is not reported unless stated. Trade-offs and implementation Not assessed unless listed in outcomes. Iodine and minerals can fall with arsenic; not quantified unless stated. Soaking and cooking water carries the removed arsenic. Not quantified. Not assessed. Applicability and verification Import control of hijiki. 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. | |||||||||||||||||||||||||||||||||||||||||||||
| Soak dried hijiki and discard the waterhome preparation · As reported | Seaweed | tAs · Decreased | 1Ichikawa et al. 2006 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Total arsenicDecreasedLower total arsenic after soakingTotal arsenic in hijikiBefore versus after a 30-minute soak (one origin, duplicate samples)Dry weightModerate · HMI calculates the relative change from the retained source means: (23100 − 32500) / 32500 × 100 = -28.9%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Arsenic eluted into soaking water as a share of the dried hijiki total. 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 A 30-minute soak in water eluted 22–32% of total arsenic, mostly as arsenate, into water that is then discarded.
Design, applicability and operating conditions Measured preparation or processing comparison. Household preparation of dried hijiki. One study family. As reported by the source Avoids high-accumulating material, or moves soluble arsenic into water that is discarded. Source measurements and linked outcomes
Three origins, duplicate samples; residue after soaking computed from eluted arsenic. Percentages as reported or computed from the source table means where stated. Concentrations stay on the source basis; mass yield is not reported unless stated. Trade-offs and implementation Not assessed unless listed in outcomes. Iodine and minerals can fall with arsenic; not quantified unless stated. Soaking and cooking water carries the removed arsenic. Not quantified. Not assessed. Applicability and verification Household preparation of dried hijiki. 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. | |||||||||||||||||||||||||||||||||||||||||||||
| Boil soaked hijiki and discard the waterhome preparation · As reported | Seaweed | tAs · Decreased | 1Ichikawa et al. 2006 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Total arsenicDecreasedLower total arsenic after soaking and boilingTotal arsenic remaining in hijikiBefore versus after soak and boil (one origin, duplicate samples)Dry weightHigh · HMI calculates the relative change from the retained source means: (6000 − 32500) / 32500 × 100 = -81.5%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Arsenic eluted into cooking water as a share of the dried hijiki total. 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 the soaked hijiki for 20 minutes at 90 °C eluted a further 53–62% of total arsenic, mostly arsenate.
Design, applicability and operating conditions Measured preparation or processing comparison. Household preparation of dried hijiki. One study family. As reported by the source Avoids high-accumulating material, or moves soluble arsenic into water that is discarded. Source measurements and linked outcomes
The residue was not speciated. Percentages as reported or computed from the source table means where stated. Concentrations stay on the source basis; mass yield is not reported unless stated. Trade-offs and implementation Not assessed unless listed in outcomes. Iodine and minerals can fall with arsenic; not quantified unless stated. Soaking and cooking water carries the removed arsenic. Not quantified. Not assessed. Applicability and verification Household preparation of dried hijiki. 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. | |||||||||||||||||||||||||||||||||||||||||||||
| Boil hijiki; baking nori has no effecthome preparation · As reported | Seaweed | iAs · Decreased tAs · Decreased | 1Laparra et al. 2003 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Inorganic arsenicDecreasedLower inorganic arsenic after boiling hijikiInorganic arsenicRaw versus boiled hijikiDry weightModerate · HMI calculates the relative change from the retained source means: (30600 − 54300) / 54300 × 100 = -43.6%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Total arsenicDecreasedLower total arsenic after boiling hijikiTotal arsenicRaw versus boiled hijikiDry weightModerate · HMI calculates the relative change from the retained source means: (65300 − 99400) / 99400 × 100 = -34.3%. This is a descriptive contrast of means; no confidence interval or significance test is inferred. Same product before and after preparation. 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 hijiki for 20 minutes lowered inorganic arsenic from 54.3 to 30.6 mg/kg dry weight; baking nori did not change arsenic.
Design, applicability and operating conditions Measured preparation or processing comparison. Household preparation. One study family. As reported by the source Avoids high-accumulating material, or moves soluble arsenic into water that is discarded. Source measurements and linked outcomes
One product per type. Percentages as reported or computed from the source table means where stated. Concentrations stay on the source basis; mass yield is not reported unless stated. Trade-offs and implementation Not assessed unless listed in outcomes. Iodine and minerals can fall with arsenic; not quantified unless stated. Soaking and cooking water carries the removed arsenic. Not quantified. Not assessed. Applicability and verification Household preparation. 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. | |||||||||||||||||||||||||||||||||||||||||||||
| Prepare kelp as soup or soak rather than a brief blanchhome preparation · As reported | Seaweed | iAs · Decreased | 1Ownsworth et al. 2019 HMI source record · Original source One dataset family. Linked analytes, repeated seasons and reports are not independent studies. Effects and comparators Inorganic arsenicDecreasedLower inorganic arsenic in the solid seaweedInorganic arsenic lossSoup preparation (75–96% loss)Dry 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. Same seaweed before and after each preparation. 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 A soup preparation removed 75–96% of inorganic arsenic from the solid seaweed, a cold soak about 65% and a 10–20 second blanch 3–61%; the arsenic moved into the liquid.
Design, applicability and operating conditions Measured preparation or processing comparison. Kelp eaten after soaking or cooking; the soup liquid keeps the arsenic. One study family. As reported by the source Avoids high-accumulating material, or moves soluble arsenic into water that is discarded. Source measurements and linked outcomes
Few samples; ranges as reported. Percentages as reported or computed from the source table means where stated. Concentrations stay on the source basis; mass yield is not reported unless stated. Trade-offs and implementation Not assessed unless listed in outcomes. Iodine and minerals can fall with arsenic; not quantified unless stated. Soaking and cooking water carries the removed arsenic. Not quantified. Not assessed. Applicability and verification Kelp eaten after soaking or cooking; the soup liquid keeps the arsenic. 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 failure modes
Choosing the lowest arsenic type can raise cadmium. Nori and wakame, the usual low inorganic arsenic choices, carried the highest cadmium means in European data (1.3–1.7 mg/kg dried).5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source → Kombu is lower in cadmium but includes oarweed, one of the highest inorganic arsenic kelps.4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →
Preparation trades contaminant removal for nutrients and flavour.11Tracing the natural and anthropogenic influence on the trace elemental chemistry of estuarine macroalgae and the implications for human consumptionScience of the Total EnvironmentRead source →12Pulsed electric field processing as an alternative to warm water treatment for the reduction of potentially toxic elements in Saccharina latissimaJournal of Applied PhycologyRead source → Boiling removes 50–90% of iodine from sugar kelp along with arsenic, and soaking water from hijiki carried 3 mg/kg inorganic arsenic, so it must not be reused for cooking.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source → Farming is not a guaranteed fix: farmed and wild sugar kelp in New England had similar cadmium and total arsenic exceedance rates.6Evidence of elevated heavy metals concentrations in wild and farmed sugar kelp (Saccharina latissima) in New EnglandScientific ReportsRead source →
Sampling and testing seaweed for heavy metals
A useful seaweed test must report inorganic arsenic by a speciation method, not total arsenic alone.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →8Arsenic speciation in edible alga samples by microwave-assisted extraction and high performance liquid chromatography coupled to atomic fluorescence spectrometryAnalytica Chimica ActaRead source → Total arsenic in kombu is typically 40–60 mg/kg as sold while inorganic arsenic is around 0.2 mg/kg, so a total arsenic result cannot show whether a product meets an inorganic arsenic limit.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →3Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaFood Standards Australia New Zealand (FSANZ), Survey reportRead source → Methods also differ in what they count as inorganic: some studies measured only water-extractable arsenate, which understates inorganic arsenic in hijiki, where 47% of the arsenic in a reference material was not extracted.25Speciation Analysis of Arsenics in Commercial Hijiki by High Performance Liquid Chromatography-tandem-mass Spectrometry and High Performance Liquid Chromatography-inductively Coupled Plasma Mass SpectrometryJournal of Health Science 56(1):47-56Read source →28A New Candidate Reference Material for Inorganic Arsenic and Arsenosugars in Hijiki Seaweed: First Results from an Inter-laboratory StudyAnalytical Sciences 2020, 36, 233–239Read source →
State the basis on every result: dry weight, dried product as sold, or fresh weight.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →16Australia New Zealand Food Standards Code - Schedule 19 - Maximum levels of contaminants and natural toxicantsFederal Register of Legislation, Authorised Version F2024C00908Read source → Australian and New Zealand limits are written at 85% hydration, so a dried hijiki result of 7.8 mg/kg corresponds to about 1.4 mg/kg at that basis.3Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaFood Standards Australia New Zealand (FSANZ), Survey reportRead source →16Australia New Zealand Food Standards Code - Schedule 19 - Maximum levels of contaminants and natural toxicantsFederal Register of Legislation, Authorised Version F2024C00908Read source → Several surveys reported values below their own detection limits or reference-material recoveries far from certified values; those results are held here and should not be used to clear a lot.18Human Exposure to Toxic Metals (Cd, Pb, Hg) and Nitrates (NO3−) from Seaweed ConsumptionApplied SciencesRead source →19Effect of thermal processing on toxic heavy metals in edible seaweeds of Gulf of Mannar and their health risk assessmentRegional Studies in Marine ScienceRead source →
Why is total arsenic not enough for seaweed?
Because most seaweed arsenic is organic.8Arsenic speciation in edible alga samples by microwave-assisted extraction and high performance liquid chromatography coupled to atomic fluorescence spectrometryAnalytica Chimica ActaRead source →9Concentrations and speciation of arsenic in New England seaweed species harvested for food and agricultureChemosphereRead source → In GEMS/Food, dried kombu had a median of 47 mg/kg total arsenic but 0.23 mg/kg inorganic arsenic, so total arsenic overstates the inorganic form about two-hundredfold in that product.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → Only hijiki and a few kelps carry inorganic arsenic at a large share of the total.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →
Procurement and process control
Specify the seaweed type and, for kelp, the species, and require inorganic arsenic results for hijiki, Sargassum products and Laminaria digitata.3Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaFood Standards Australia New Zealand (FSANZ), Survey reportRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →13High proportions of inorganic arsenic in Laminaria digitata but not in Ascophyllum nodosum samples from IrelandChemosphereRead source → Limits differ by market: Australia and New Zealand set 1 mg/kg inorganic arsenic for seaweed at 85% hydration, Singapore 2 ppm inorganic arsenic and 2 ppm cadmium for seaweed, and Thailand 2 mg/kg cadmium for dried seaweed.16Australia New Zealand Food Standards Code - Schedule 19 - Maximum levels of contaminants and natural toxicantsFederal Register of Legislation, Authorised Version F2024C00908Read source →29Food Regulations: regulation 31 heavy metals, arsenic and leadSingapore Statutes OnlineRead source →30Notification of Ministry of Public Health (No. 414) B.E. 2563: Standards for Contaminants in FoodGovernment Gazette Vol. 137, Special Part 118 NgorRead source → China sets lead at 0.5 mg/kg for fresh algae and 1.0 mg/kg for algae products, and the EU sets nickel at 30 mg/kg for seaweed and 40 mg/kg for wakame from July 2025.31GB 2762-2022 National Food Safety Standard: Maximum Levels of Contaminants in FoodsNational Food Safety Standard GB 2762-2022Read source →32Commission Regulation (EU) 2024/1987 of 30 July 2024 amending Regulation (EU) 2023/915 as regards maximum levels of nickel in certain foodstuffsOfficial Journal of the European Union, L series, 2024/1987 (31.7.2024)Read source →
The EU has no general cadmium, lead or arsenic limit for seaweed food; its 3.0 mg/kg cadmium limit applies to supplements made at least 80% from dried seaweed.33Commission 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 → Ask for cadmium results on nori, laver and wakame, which most often approach the 2 mg/kg limits used in Singapore and Thailand.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →26Total arsenic, mercury, lead, and cadmium contents in edible dried seaweed in KoreaFood Additives & Contaminants: Part B: SurveillanceRead source →29Food Regulations: regulation 31 heavy metals, arsenic and leadSingapore Statutes OnlineRead source →30Notification of Ministry of Public Health (No. 414) B.E. 2563: Standards for Contaminants in FoodGovernment Gazette Vol. 137, Special Part 118 NgorRead source → Record growing area separately from the packing or purchase market, because most monitoring identifies only the market.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →
Finished-product and exposure implications
Seaweed is eaten in small portions, so concentration alone does not set exposure.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →34Dietary Lead Exposure and Associated Health Risks in Guangzhou, ChinaInternational Journal of Environmental Research and Public HealthRead source → In European consumption data, seaweed added little to population cadmium exposure, but adult seaweed consumers reached a mean of 3.1 µg/kg body weight per week of cadmium, mainly from laver.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source → In Guangzhou, algae supplied 4.7% of dietary lead overall and 7.1% for people aged 60 and over, and in China seaweed supplied 2.4% of dietary cadmium.35Dietary cadmium exposure assessment among the Chinese populationPLoS ONE 12(5): e0177978Read source →34Dietary Lead Exposure and Associated Health Risks in Guangzhou, ChinaInternational Journal of Environmental Research and Public HealthRead source →
Hijiki changes the picture for inorganic arsenic. EFSA estimated that adult high consumers of hijiki eating 10 g a day of prepared hijiki would take in about 1.6 µg/kg body weight per day of inorganic arsenic.36Dietary exposure to inorganic arsenic in the European populationEFSA Journal 2014;12(3):3597Read source → A Spanish survey calculated that 1.7 g a day of one dried hijiki product would reach the former WHO tolerable weekly intake for inorganic arsenic.37Heavy Metal, Total Arsenic, and Inorganic Arsenic Contents of Algae Food ProductsJournal of Agricultural and Food ChemistryRead source →
Kelp supplements are concentrated: one Belgian kelp product carried 4.7 mg/kg inorganic arsenic, and seaweed supplements are covered by the EU 3.0 mg/kg cadmium limit.14Intake of food supplements based on algae or cyanobacteria may pose a health risk due to elevated concentrations of arsenic speciesFood Additives & Contaminants: Part ARead source →33Commission 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 → Foods that contain seaweed were not measured together with the seaweed in them, so a product result cannot be attributed to its seaweed content.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →38Results of the BfR MEAL Study: In Germany, mercury is mostly contained in fish and seafood while cadmium, lead, and nickel are present in a broad spectrum of foodsFood Chemistry: XRead source →
Evidence review, methods and research gaps
This assessment covers every source record in the HMI library that is tagged to seaweed or names it, plus every seaweed row in WHO GEMS/Food and the HMI indexes; each has a recorded decision based on its content. Seventy-eight sources contribute table rows; most others are reviews, mentions of microalgae, or incidental matches.21Risks and benefits of consuming edible seaweedsNutrition ReviewsRead source →23Arsenic in edible macroalgae: an integrated approachJournal of Toxicology and Environmental Health, Part B: Critical ReviewsRead source → Fifty-four rows from twelve sources are held because their values contradict their own methods or tables.18Human Exposure to Toxic Metals (Cd, Pb, Hg) and Nitrates (NO3−) from Seaweed ConsumptionApplied SciencesRead source →19Effect of thermal processing on toxic heavy metals in edible seaweeds of Gulf of Mannar and their health risk assessmentRegional Studies in Marine ScienceRead source →20Elevated Concentrations of Metal(loids) in Seaweed and the Concomitant Exposure to HumansFoodsRead source →
Gaps remain. Few studies follow the same lots through commercial processing, few report growing origin for retail products, and the Vietnamese supplement standard could not be located.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →12Pulsed electric field processing as an alternative to warm water treatment for the reduction of potentially toxic elements in Saccharina latissimaJournal of Applied PhycologyRead source →25Speciation Analysis of Arsenics in Commercial Hijiki by High Performance Liquid Chromatography-tandem-mass Spectrometry and High Performance Liquid Chromatography-inductively Coupled Plasma Mass SpectrometryJournal of Health Science 56(1):47-56Read source → Several compilations, such as Japanese cumulative arsenic data, repeat values from primary studies and are treated as context to avoid double counting.39Arsenic in various foods: Cumulative dataFood Additives & ContaminantsRead source →40Arsenic in Seafood: Speciation Issues for Human Health Risk AssessmentHuman and Ecological Risk AssessmentRead source →41Arsenic in Herbal Kelp Supplements: Concentration, Regulations, and LabelingEnvironmental Health PerspectivesRead 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.
Seaweed FAQs
What heavy metals are found in seaweed?
Arsenic, cadmium, lead and mercury are measured in most seaweed surveys, and arsenic is present at the highest concentrations.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source → Most of that arsenic is organic; inorganic arsenic is high mainly in hijiki and a few kelps, while cadmium is highest in laver and wakame.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →
How do heavy metals get into seaweed?
Seaweed absorbs metals from the surrounding seawater through its whole surface.4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →21Risks and benefits of consuming edible seaweedsNutrition ReviewsRead source → Brown seaweeds take up arsenate like phosphate and turn most of it into arsenosugars, while hijiki keeps much of it as inorganic arsenic.22Arsenic contents and speciation at different growth stages of Sargassum fusiforme [Harv.] Setchell (Hijiki), an edible seaweedApplied Ecology and Environmental ResearchRead source →8Arsenic speciation in edible alga samples by microwave-assisted extraction and high performance liquid chromatography coupled to atomic fluorescence spectrometryAnalytica Chimica ActaRead source →
Is organic seaweed free from heavy metals?
No source in the library compares organic-certified and conventional seaweed, so there is no evidence that an organic label lowers metals. Metal levels follow the seaweed type and the water it grew in, which certification does not control.4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →17Chemical contaminant levels in edible seaweeds of the Salish Sea and implications for their consumptionPLOS ONERead source →
Which types of seaweed have the lowest levels?
For inorganic arsenic, nori, wakame, dulse and Saccharina kombu were lowest, and hijiki highest.3Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaFood Standards Australia New Zealand (FSANZ), Survey reportRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source → For cadmium, kombu and dulse were lower than laver and wakame, so no type is lowest for every metal.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →
Which regions produce seaweed with the lowest levels?
Origin comparisons are few. One Canary Islands survey found Galician kombu and wakame lower in cadmium than Asian products, and Korean west-coast laver higher than south-coast laver, but species differences are far larger than these origin differences.18Human Exposure to Toxic Metals (Cd, Pb, Hg) and Nitrates (NO3−) from Seaweed ConsumptionApplied SciencesRead source →26Total arsenic, mercury, lead, and cadmium contents in edible dried seaweed in KoreaFood Additives & Contaminants: Part B: SurveillanceRead source →
Do products made from seaweed also contain heavy metals?
Seaweed supplements can, because they are concentrated dried seaweed: one Belgian kelp supplement carried 4.7 mg/kg inorganic arsenic.14Intake of food supplements based on algae or cyanobacteria may pose a health risk due to elevated concentrations of arsenic speciesFood Additives & Contaminants: Part ARead source → Foods that contain seaweed, such as snacks or sushi, were not measured together with their seaweed, so their results cannot be attributed to it.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →38Results of the BfR MEAL Study: In Germany, mercury is mostly contained in fish and seafood while cadmium, lead, and nickel are present in a broad spectrum of foodsFood Chemistry: XRead source →
What do the levels in seaweed mean for health?
For most people seaweed adds little to metal intake because portions are small.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →35Dietary cadmium exposure assessment among the Chinese populationPLoS ONE 12(5): e0177978Read source → Regular hijiki eaters are the exception: EFSA estimated about 1.6 µg/kg body weight per day of inorganic arsenic for high consumers, and several food agencies advise against eating hijiki.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →36Dietary exposure to inorganic arsenic in the European populationEFSA Journal 2014;12(3):3597Read source →42Chronic dietary exposure to inorganic arsenicEFSA JournalRead source →
Are there legal limits for heavy metals in seaweed?
Yes, in some markets: Australia and New Zealand set 1 mg/kg inorganic arsenic at 85% hydration, Singapore 2 ppm inorganic arsenic and cadmium, Thailand 2 mg/kg cadmium for dried seaweed, and China 0.5–1.0 mg/kg lead for algae.16Australia New Zealand Food Standards Code - Schedule 19 - Maximum levels of contaminants and natural toxicantsFederal Register of Legislation, Authorised Version F2024C00908Read source →29Food Regulations: regulation 31 heavy metals, arsenic and leadSingapore Statutes OnlineRead source →30Notification of Ministry of Public Health (No. 414) B.E. 2563: Standards for Contaminants in FoodGovernment Gazette Vol. 137, Special Part 118 NgorRead source →31GB 2762-2022 National Food Safety Standard: Maximum Levels of Contaminants in FoodsNational Food Safety Standard GB 2762-2022Read source → The EU limits nickel in seaweed (30 mg/kg, wakame 40 mg/kg) and cadmium in seaweed supplements (3.0 mg/kg).32Commission Regulation (EU) 2024/1987 of 30 July 2024 amending Regulation (EU) 2023/915 as regards maximum levels of nickel in certain foodstuffsOfficial Journal of the European Union, L series, 2024/1987 (31.7.2024)Read source →33Commission 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 →
Can soaking or cooking remove heavy metals from seaweed?
Soaking and boiling remove much of the arsenic, especially from hijiki, as long as the water is thrown away.7Decrease of arsenic in edible brown algae Hijikia fusiforme by the cooking processApplied Organometallic ChemistryRead source →10Estimation of Arsenic Bioaccessibility in Edible Seaweed by an in Vitro Digestion MethodJournal of Agricultural and Food ChemistryRead source →11Tracing the natural and anthropogenic influence on the trace elemental chemistry of estuarine macroalgae and the implications for human consumptionScience of the Total EnvironmentRead source → They do little for cadmium and lead, which stayed the same or rose on a dry-weight basis after processing sugar kelp.12Pulsed electric field processing as an alternative to warm water treatment for the reduction of potentially toxic elements in Saccharina latissimaJournal of Applied PhycologyRead source →27Improving nutritional intakes and reducing metal(loid) exposures from wild fish broth among Inuit pregnant womenScience of the Total EnvironmentRead source →
What is the difference between total and inorganic arsenic in seaweed?
Total arsenic counts every form, and in seaweed most of it is organic arsenosugars, which are much less toxic than inorganic arsenic.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →8Arsenic speciation in edible alga samples by microwave-assisted extraction and high performance liquid chromatography coupled to atomic fluorescence spectrometryAnalytica Chimica ActaRead source → Limits and health assessments for seaweed are written for inorganic arsenic, so a total arsenic result alone cannot show compliance.16Australia New Zealand Food Standards Code - Schedule 19 - Maximum levels of contaminants and natural toxicantsFederal Register of Legislation, Authorised Version F2024C00908Read source →29Food Regulations: regulation 31 heavy metals, arsenic and leadSingapore Statutes OnlineRead source →
Should pregnant women or children avoid any seaweed?
The supported advice concerns hijiki: food agencies in the United Kingdom, Australia and New Zealand advised against eating it because of its inorganic arsenic.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →42Chronic dietary exposure to inorganic arsenicEFSA JournalRead source → A review also cites Australian and New Zealand advice for pregnant women to limit brown seaweed to one portion a week.21Risks and benefits of consuming edible seaweedsNutrition ReviewsRead source →
Should I stop eating seaweed?
The evidence supports avoiding hijiki, not seaweed in general.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source → Nori, wakame and kombu measured far lower in inorganic arsenic, though nori and wakame carry more cadmium.3Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaFood Standards Australia New Zealand (FSANZ), Survey reportRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →
Why is hijiki so much higher in arsenic than other seaweeds?
Hijiki keeps much of the arsenic it absorbs as inorganic arsenate instead of converting it to arsenosugars.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →8Arsenic speciation in edible alga samples by microwave-assisted extraction and high performance liquid chromatography coupled to atomic fluorescence spectrometryAnalytica Chimica ActaRead source → About 60–70% of its total arsenic is inorganic, against under 1% in most kelp and nori.1Arsenic in seaweed—Forms, concentration and dietary exposureFood and Chemical ToxicologyRead source →9Concentrations and speciation of arsenic in New England seaweed species harvested for food and agricultureChemosphereRead source →
Is kelp or kombu high in arsenic?
Kombu is high in total arsenic but usually low in inorganic arsenic, around 0.2 mg/kg as sold.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →3Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaFood Standards Australia New Zealand (FSANZ), Survey reportRead source → Oarweed (Laminaria digitata) is the exception, with 8–62 mg/kg inorganic arsenic dry weight in studies from Norway, Ireland and Maine.4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →9Concentrations and speciation of arsenic in New England seaweed species harvested for food and agricultureChemosphereRead source →13High proportions of inorganic arsenic in Laminaria digitata but not in Ascophyllum nodosum samples from IrelandChemosphereRead source →
Is nori high in cadmium?
Nori is among the higher cadmium seaweeds.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →26Total arsenic, mercury, lead, and cadmium contents in edible dried seaweed in KoreaFood Additives & Contaminants: Part B: SurveillanceRead source → Dried laver averaged 1.68 mg/kg in European monitoring and Korean laver 0.61 mg/kg dry weight, near or above the 0.5–2 mg/kg limits used in some markets.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →26Total arsenic, mercury, lead, and cadmium contents in edible dried seaweed in KoreaFood Additives & Contaminants: Part B: SurveillanceRead source →29Food Regulations: regulation 31 heavy metals, arsenic and leadSingapore Statutes OnlineRead source →
Is fresh seaweed lower in metals than dried?
Fresh seaweed has lower concentrations per kilogram only because it is mostly water.3Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaFood Standards Australia New Zealand (FSANZ), Survey reportRead source →5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source → European fresh kombu averaged 0.20 mg/kg cadmium against 0.46 mg/kg for dried kombu, which reflects water content rather than a cleaner product.5Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →
Is farmed seaweed lower in metals than wild?
Not consistently. Farmed and wild sugar kelp in New England had similar cadmium and total arsenic, and farmed sugar kelp in northern Norway carried more cadmium than southern farms.4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →6Evidence of elevated heavy metals concentrations in wild and farmed sugar kelp (Saccharina latissima) in New EnglandScientific ReportsRead source →
Does seaweed contain mercury?
Usually very little.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source → Most dried-seaweed mercury results in GEMS/Food were below a 50 µg/kg detection limit, and Norwegian medians were 0.005–0.024 mg/kg dry weight.2GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →4Knowledge update on macroalgae food and feed safetyRapport fra HavforskningenRead source →
Are kelp supplements a concern?
They can be, because supplements are dried seaweed taken daily.14Intake of food supplements based on algae or cyanobacteria may pose a health risk due to elevated concentrations of arsenic speciesFood Additives & Contaminants: Part ARead source →15Improved Arsenic Speciation Analysis for Extracts of Commercially Available Edible Marine Algae Using HPLC-ES-MS/MSJournal of Agricultural and Food Chemistry 54(18):6507-6519Read source → Belgian kelp supplements ranged from 0.07 to 4.7 mg/kg inorganic arsenic, and the EU caps cadmium at 3.0 mg/kg in supplements made mainly from seaweed.14Intake of food supplements based on algae or cyanobacteria may pose a health risk due to elevated concentrations of arsenic speciesFood Additives & Contaminants: Part ARead source →33Commission 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 →
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.
- Arsenic in seaweed—Forms, concentration and dietary exposurePeer-reviewed
- GEMS/Food Contaminants database heavy-metal exportsDataset
- Survey of Inorganic Arsenic in Seaweed and Seaweed-Containing Products Available in AustraliaGovernment
- Knowledge update on macroalgae food and feed safetyGovernment
- Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationPeer-reviewed
- Evidence of elevated heavy metals concentrations in wild and farmed sugar kelp (Saccharina latissima) in New EnglandPeer-reviewed
- Decrease of arsenic in edible brown algae Hijikia fusiforme by the cooking processPeer-reviewed
- Arsenic speciation in edible alga samples by microwave-assisted extraction and high performance liquid chromatography coupled to atomic fluorescence spectrometryPeer-reviewed
- Concentrations and speciation of arsenic in New England seaweed species harvested for food and agriculturePeer-reviewed
- Estimation of Arsenic Bioaccessibility in Edible Seaweed by an in Vitro Digestion MethodPeer-reviewed
- Tracing the natural and anthropogenic influence on the trace elemental chemistry of estuarine macroalgae and the implications for human consumptionPeer-reviewed
- Pulsed electric field processing as an alternative to warm water treatment for the reduction of potentially toxic elements in Saccharina latissimaPeer-reviewed
- High proportions of inorganic arsenic in Laminaria digitata but not in Ascophyllum nodosum samples from IrelandPeer-reviewed
- Intake of food supplements based on algae or cyanobacteria may pose a health risk due to elevated concentrations of arsenic speciesPeer-reviewed
- Improved Arsenic Speciation Analysis for Extracts of Commercially Available Edible Marine Algae Using HPLC-ES-MS/MSPeer-reviewed
- Australia New Zealand Food Standards Code - Schedule 19 - Maximum levels of contaminants and natural toxicantsRegulation
- Chemical contaminant levels in edible seaweeds of the Salish Sea and implications for their consumptionPeer-reviewed
- Human Exposure to Toxic Metals (Cd, Pb, Hg) and Nitrates (NO3−) from Seaweed ConsumptionPeer-reviewed
- Effect of thermal processing on toxic heavy metals in edible seaweeds of Gulf of Mannar and their health risk assessmentPeer-reviewed
- Elevated Concentrations of Metal(loids) in Seaweed and the Concomitant Exposure to HumansPeer-reviewed
- Risks and benefits of consuming edible seaweedsReview
- Arsenic contents and speciation at different growth stages of Sargassum fusiforme Harv. Setchell (Hijiki), an edible seaweedPeer-reviewed
- Arsenic in edible macroalgae: an integrated approachReview
- Determination of Inorganic Arsenic in Seaweed and Seafood by LC-ICP-MS: Method ValidationPeer-reviewed
- Speciation Analysis of Arsenics in Commercial Hijiki by High Performance Liquid Chromatography-tandem-mass Spectrometry and High Performance Liquid Chromatography-inductively Coupled Plasma Mass SpectrometryPeer-reviewed
- Total arsenic, mercury, lead, and cadmium contents in edible dried seaweed in KoreaPeer-reviewed
- Improving nutritional intakes and reducing metal(loid) exposures from wild fish broth among Inuit pregnant womenPeer-reviewed
- A New Candidate Reference Material for Inorganic Arsenic and Arsenosugars in Hijiki Seaweed: First Results from an Inter-laboratory StudyPeer-reviewed
- Food Regulations: regulation 31 heavy metals, arsenic and leadRegulation
- Notification of Ministry of Public Health (No. 414) B.E. 2563: Standards for Contaminants in FoodRegulation
- GB 2762-2022 National Food Safety Standard: Maximum Levels of Contaminants in FoodsRegulation
- Commission Regulation (EU) 2024/1987 of 30 July 2024 amending Regulation (EU) 2023/915 as regards maximum levels of nickel in certain foodstuffsRegulation
- Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006Regulation
- Dietary Lead Exposure and Associated Health Risks in Guangzhou, ChinaPeer-reviewed
- Dietary cadmium exposure assessment among the Chinese populationPeer-reviewed
- Dietary exposure to inorganic arsenic in the European populationGovernment
- Heavy Metal, Total Arsenic, and Inorganic Arsenic Contents of Algae Food ProductsPeer-reviewed
- Results of the BfR MEAL Study: In Germany, mercury is mostly contained in fish and seafood while cadmium, lead, and nickel are present in a broad spectrum of foodsPeer-reviewed
- Arsenic in various foods: Cumulative dataPeer-reviewed
- Arsenic in Seafood: Speciation Issues for Human Health Risk AssessmentReview
- Arsenic in Herbal Kelp Supplements: Concentration, Regulations, and LabelingPeer-reviewed
- Chronic dietary exposure to inorganic arsenicGovernment
Sources
Browse Seaweed 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 seaweed record in the library: WHO GEMS/Food monitoring results, survey, agency and processing studies, pooled seaweed comparisons kept separate by metal and basis, verified limits and stage-led controls.
