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Heavy Metal Index
A bowl of dried kelp seaweed, a dish of dark green spirulina powder and a stack of dried nori sheets.

Heavy metals in Algae

Lead, cadmium, total arsenic, inorganic arsenic and total mercury in algae: monitoring results, studies, references by form and basis, limits, testing and controls.

Quick read

Algae in the HMI library has 221 reported results for lead, cadmium, total arsenic, inorganic arsenic, dimethylarsinic acid, monomethylarsonic acid, total mercury, methylmercury, chromium, aluminium, arsenosugar (glycerol sugar), arsenosugar (phosphate sugar), arsenosugar (sulfate sugar), arsenosugar (sulfonate sugar), As(III), As(V), AsB, I, TETRA, TMAO and water-extractable As from 14 sources.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2European Food Safety Authority (EFSA), Dujardin B, Ferreira de Sousa R, Gomez Ruiz JA · 2023Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →3Fechner C, Hackethal C, Höpfner T, Dietrich J, Bloch D, Lindtner O, Sarvan I · 2022Results 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 →4EFSA Panel on Contaminants in the Food Chain (CONTAM) · 2010Scientific Opinion on Lead in FoodEFSA Journal 2010;8(4):1570Read source →5Kim DY, Jeon H, Shin HS · 2023Risk Assessment and Determination of Arsenic and Heavy Metals in Fishery Products in KoreaFoodsRead source →6Wang M, Liang B, Zhang W, Chen K, Zhang Y, Zhou H, Cheng Y, Liu H, Zhong X, Li Y, Liu Y · 2019Dietary Lead Exposure and Associated Health Risks in Guangzhou, ChinaInternational Journal of Environmental Research and Public HealthRead source →

Algae overview

Algae in the HMI library has 221 reported results for lead, cadmium, total arsenic, inorganic arsenic, dimethylarsinic acid, monomethylarsonic acid, total mercury, methylmercury, chromium, aluminium, arsenosugar (glycerol sugar), arsenosugar (phosphate sugar), arsenosugar (sulfate sugar), arsenosugar (sulfonate sugar), As(III), As(V), AsB, I, TETRA, TMAO and water-extractable As from 14 sources.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2European Food Safety Authority (EFSA), Dujardin B, Ferreira de Sousa R, Gomez Ruiz JA · 2023Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →3Fechner C, Hackethal C, Höpfner T, Dietrich J, Bloch D, Lindtner O, Sarvan I · 2022Results 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 →4EFSA Panel on Contaminants in the Food Chain (CONTAM) · 2010Scientific Opinion on Lead in FoodEFSA Journal 2010;8(4):1570Read source →5Kim DY, Jeon H, Shin HS · 2023Risk Assessment and Determination of Arsenic and Heavy Metals in Fishery Products in KoreaFoodsRead source →6Wang M, Liang B, Zhang W, Chen K, Zhang Y, Zhou H, Cheng Y, Liu H, Zhong X, Li Y, Liu Y · 2019Dietary Lead Exposure and Associated Health Risks in Guangzhou, ChinaInternational Journal of Environmental Research and Public HealthRead source → WHO GEMS/Food submissions reported lead in algae, as sold from 18 results in 2 reporting regions, with subgroup medians below 50 µg/kg, mostly non-detects.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → For cadmium, GEMS/Food gave a subgroup median of 40 µg/kg from 17 results.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →

Across 2 other studies of ordinary farms and markets, reported lead means and medians on an as-sold or fresh-weight basis ranged from 55 µg/kg (Fechner et al. 2022) to 890 µg/kg (European Food Safety Authority (EFSA) 2023).2European Food Safety Authority (EFSA), Dujardin B, Ferreira de Sousa R, Gomez Ruiz JA · 2023Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →3Fechner C, Hackethal C, Höpfner T, Dietrich J, Bloch D, Lindtner O, Sarvan I · 2022Results 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 → For cadmium, 2 studies on an as-sold or fresh-weight basis reported means and medians from 109 µg/kg (European Food Safety Authority (EFSA) 2023) to 1,090 µg/kg (European Food Safety Authority (EFSA) 2023).2European Food Safety Authority (EFSA), Dujardin B, Ferreira de Sousa R, Gomez Ruiz JA · 2023Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →

For a buyer the practical points are the form bought, the basis a result is reported on, where the algae came from and the laboratory’s reporting limit. Testing finds contamination but does not remove it.

What counts as algae

This page covers algae in 4 forms kept separate in every comparison: algae, as sold (113 results), algae, dried (80 results), algae, powder or ground (27 results) and algae, flour or meal (1 result).1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2European Food Safety Authority (EFSA), Dujardin B, Ferreira de Sousa R, Gomez Ruiz JA · 2023Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →3Fechner C, Hackethal C, Höpfner T, Dietrich J, Bloch D, Lindtner O, Sarvan I · 2022Results 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 →4EFSA Panel on Contaminants in the Food Chain (CONTAM) · 2010Scientific Opinion on Lead in FoodEFSA Journal 2010;8(4):1570Read source →5Kim DY, Jeon H, Shin HS · 2023Risk Assessment and Determination of Arsenic and Heavy Metals in Fishery Products in KoreaFoodsRead source →6Wang M, Liang B, Zhang W, Chen K, Zhang Y, Zhou H, Cheng Y, Liu H, Zhong X, Li Y, Liu Y · 2019Dietary Lead Exposure and Associated Health Risks in Guangzhou, ChinaInternational Journal of Environmental Research and Public HealthRead source →

Results stay on the basis each source reports: as sold or fresh weight, dry weight, or unstated. Dry-weight, as-sold and unstated results are never pooled, and no moisture conversion is applied.

Heavy metal contamination profile of algae

The table holds every extracted algae result: one row for each statistic a source reports for a form, group and metal, 221 rows in all, grouped by metal and form; percentiles, ranges and maxima for the same samples as a mean or median are shown on that row.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2European Food Safety Authority (EFSA), Dujardin B, Ferreira de Sousa R, Gomez Ruiz JA · 2023Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →3Fechner C, Hackethal C, Höpfner T, Dietrich J, Bloch D, Lindtner O, Sarvan I · 2022Results 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 →4EFSA Panel on Contaminants in the Food Chain (CONTAM) · 2010Scientific Opinion on Lead in FoodEFSA Journal 2010;8(4):1570Read source →5Kim DY, Jeon H, Shin HS · 2023Risk Assessment and Determination of Arsenic and Heavy Metals in Fishery Products in KoreaFoodsRead source →6Wang M, Liang B, Zhang W, Chen K, Zhang Y, Zhou H, Cheng Y, Liu H, Zhong X, Li Y, Liu Y · 2019Dietary Lead Exposure and Associated Health Risks in Guangzhou, ChinaInternational Journal of Environmental Research and Public HealthRead source → Monitoring medians are HMI calculations from individual submissions; non-detects remain intervals between zero and the reporting limit and are never read as zero.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →

99 rows can be rated against an HMI reference for the same form and basis, 0 rows have a direct same-study comparison, and the rest stay unrated with the reason recorded. 1 value from 1 source failed a check against their own source and are shown but not compared.7Lin P, Nan FH, Ling MP · 2021Dietary Exposure of the Taiwan Population to Mercury Content in Various Seafood Assessed by a Total Diet StudyInternational Journal of Environmental Research and Public HealthRead source →

Comparison methods and scope

Each row is one statistic a source reports for one form of algae, group and metal; percentiles, ranges and maxima reported for the same samples as a mean or median are shown on that row. Different forms and preparation states are kept apart, and dry-weight results never share a reference with as-sold or fresh-weight results. Ratings place a result against an HMI reference built from monitoring results and ordinary-setting medians for the same form and basis. Same-study contrasts compare a contaminated or treated site with its control, targeted with random sampling, a prepared form with the unprocessed one, or one group of a study with the median of its other groups. Held rows failed a check against their own source and are shown but not compared.

About this table
Food formCollection scopeFindingComparisonEvidence
Algae findings from monitoring programmes, total diet studies and every extracted field, market and contaminated-site study, in µg/kg with each source’s form, basis, statistic and censoring retained.
Food formCollection scopeFinding (µg/kg)ComparisonEvidence
27 findings · 6 studies · 13 spread figures folded in
Algae, as soldWHO GEMS/FoodWPRO2024As sold / freshmedian.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldFechner et al. 2022all samples (Germany, national)2017–2019As sold / freshmean.
Algae, as soldWHO GEMS/FoodEURO2015median.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2010Miscellaneous products and products for special dietary use2000–2009Basis not statedmax.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2010Miscellaneous products and products for special dietary use2000–2009Basis not statedmax.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2010Miscellaneous products and products for special dietary use2000–2009Basis not statedmax.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2010Miscellaneous products and products for special dietary use2000–2009Basis not statedmedian.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2010Miscellaneous products and products for special dietary use2000–2009Basis not statedmedian.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2010Miscellaneous products and products for special dietary use2000–2009Basis not statedmedian.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2010Miscellaneous products and products for special dietary use2000–2009Basis not statedmean.Same samples: 0 µg/kg (percentile); 1,100 µg/kg (percentile); 4,190 µg/kg (percentile); 1,700 µg/kg (percentile)
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2010Miscellaneous products and products for special dietary use2000–2009Basis not statedmean.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2010Miscellaneous products and products for special dietary use2000–2009Basis not statedmean.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2010Miscellaneous products and products for special dietary use2000–2009Basis not statedmedian.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2010Miscellaneous products and products for special dietary use2000–2009Basis not statedmedian.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2010Miscellaneous products and products for special dietary use2000–2009Basis not statedmedian.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2010Miscellaneous products and products for special dietary use2000–2009Basis not statedmean.Same samples: 14 µg/kg (percentile); 1,100 µg/kg (percentile); 41 µg/kg (percentile); 4,190 µg/kg (percentile); 10 µg/kg (percentile); 1,700 µg/kg (percentile)
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2010Miscellaneous products and products for special dietary use2000–2009Basis not statedmean.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2010Miscellaneous products and products for special dietary use2000–2009Basis not statedmean.
Algae, as soldKim et al. 2023all samples in category2021Basis not statedmean.
Algae, as soldKim et al. 2023Sea algae (n = 105)2021Basis not statedmin.
Algae, as soldKim et al. 2023Sea algae (n = 105)2021Basis not statedmax.
Algae, as soldWang et al. 2019all samples (Guangzhou, 2014-2017)2014–2017Basis not statedmedian.
Algae, as soldWang et al. 2019all samples (Guangzhou, 2014-2017)2014–2017Basis not statedmean.Same samples: 894 µg/kg (percentile)
11 findings · 1 study
Algae, driedAlmela et al. 2002all 18 productsCollection date unreportedrange.
Algae, driedAlmela et al. 2002retail product 1Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 2Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 3Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 4Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 5Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 6Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 7Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 8Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 9Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 18Collection date unreportedsample value.
9 findings · 4 studies
Algae, as soldWHO GEMS/FoodWPRO2024As sold / freshmedian.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldFechner et al. 2022all samples (Germany, national)2017–2019As sold / freshmean.
Algae, as soldKim et al. 2023all samples in category2021Basis not statedmean.
Algae, as soldKim et al. 2023Sea algae (n = 105)2021Basis not statedmin.
Algae, as soldKim et al. 2023Sea algae (n = 105)2021Basis not statedmax.
16 findings · 1 study
Algae, driedAlmela et al. 2002all 18 productsCollection date unreportedrange.
Algae, driedAlmela et al. 2002retail product 1Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 2Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 3Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 4Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 5Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 6Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 7Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 8Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 9Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 10Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 11Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 12Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 13Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 14Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 18Collection date unreportedsample value.
25 findings · 5 studies · 6 spread figures folded in
Algae, as soldWHO GEMS/FoodEURO2017As sold / freshmedian.
Algae, as soldWHO GEMS/FoodEURO2023As sold / freshmedian.
Algae, as soldWHO GEMS/FoodEURO2017As sold / freshmedian.
Algae, as soldWHO GEMS/FoodEURO2014–2023As sold / freshmedian.
Algae, as soldWHO GEMS/FoodEURO2014–2022As sold / freshmedian.
Algae, as soldWHO GEMS/FoodEURO2022–2023As sold / freshmedian.
Algae, as soldWHO GEMS/FoodWPRO2024As sold / freshmedian.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldWHO GEMS/FoodEURO2016–2017median.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2009EFSA 2009 pooled European occurrence dataCollection date unreportedmedian.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2009EFSA 2009 pooled European occurrence dataCollection date unreportedmedian.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2009EFSA 2009 pooled European occurrence dataCollection date unreportedmean.Same samples: 236,000 µg/kg (maximum); 116,000 µg/kg (maximum); 102,000 µg/kg (percentile); 116,000 µg/kg (percentile); 126,000 µg/kg (maximum); 4,370 µg/kg (percentile)
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2009EFSA 2009 pooled European occurrence dataCollection date unreportedmean.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2009EFSA 2009 pooled European occurrence dataCollection date unreportedmean.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2009EFSA 2009 pooled European occurrence dataCollection date unreportedmean.
Algae, as soldGarcía-Salgado et al. 2012all 12 algaeCollection date unreportedrange.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2009EFSA 2009 pooled European occurrence dataCollection date unreportedBasis not statedmedian.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2009EFSA 2009 pooled European occurrence dataCollection date unreportedBasis not statedmean.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2009EFSA 2009 pooled European occurrence dataCollection date unreportedBasis not statedmean.
Algae, as soldKim et al. 2023all samples in category2021Basis not statedmean.
Algae, as soldKim et al. 2023Sea algae (n = 105)2021Basis not statedmin.
Algae, as soldKim et al. 2023Sea algae (n = 105)2021Basis not statedmax.
17 findings · 2 studies
Algae, driedAlmela et al. 2002all 18 productsCollection date unreportedrange.
Algae, driedAlmela et al. 2002retail product 1Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 2Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 3Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 4Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 5Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 6Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 7Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 8Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 9Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 10Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 11Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 12Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 13Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 14Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 18Collection date unreportedsample value.
Algae, driedDíaz et al. 2012All 14 species (range of species means)2003–2004range.
2 findings · 1 study
Algae, powder or groundGarcía-Salgado et al. 2012Fucus (Fucus vesiculosus), FranceCollection date unreportedsample value.
Algae, powder or groundGarcía-Salgado et al. 2012Laminaria (Laminaria digitata), FranceCollection date unreportedsample value.
1 finding · 1 study
Algae, flour or mealEFSA Panel on Contaminants in the Food Chain (CONTAM) 2009Algae as foodCollection date unreportedAs sold / freshsample value.
13 findings · 3 studies
Algae, as soldWHO GEMS/FoodEURO2014–2023As sold / freshmedian.
Algae, as soldWHO GEMS/FoodEURO2018–2022As sold / freshmedian.
Algae, as soldWHO GEMS/FoodEURO2022As sold / freshmedian.
Algae, as soldWHO GEMS/FoodPAHO2014–2021As sold / freshmedian.
Algae, as soldWHO GEMS/FoodWPRO2020–2024As sold / freshmedian.
Algae, as soldWHO GEMS/FoodWPRO2020–2024As sold / freshmedian.
Algae, as soldWHO GEMS/FoodWPRO2024As sold / freshmedian.
Algae, as soldWHO GEMS/FoodWPRO2015As sold / freshmedian.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2014European dietary-survey occurrence data2003–2013Basis not statedmean.
17 findings · 2 studies
Algae, driedAlmela et al. 2002all 18 productsCollection date unreportedrange.
Algae, driedAlmela et al. 2002retail product 1Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 2Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 3Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 4Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 5Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 6Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 7Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 8Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 9Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 10Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 11Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 12Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 13Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 14Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 18Collection date unreportedsample value.
Algae, driedDíaz et al. 2012All 14 species (range of species means)2003–2004range.
2 findings · 1 study
Algae, powder or groundGarcía-Salgado et al. 2012Fucus (Fucus vesiculosus), FranceCollection date unreportedsample value.
Algae, powder or groundGarcía-Salgado et al. 2012Laminaria (Laminaria digitata), FranceCollection date unreportedsample value.
3 findings · 2 studies
Algae, as soldWHO GEMS/FoodEURO2022–2023As sold / freshmedian.
Algae, as soldWHO GEMS/FoodEURO2016median.
Algae, as soldEFSA CONTAM Panel 2024EU market, all samples in commodity2012–2022Basis not statedmean.
1 finding · 1 study
Algae, powder or groundGarcía-Salgado et al. 2012Fucus (Fucus vesiculosus), FranceCollection date unreportedsample value.
2 findings · 1 study
Algae, powder or groundGarcía-Salgado et al. 2012Fucus (Fucus vesiculosus), FranceCollection date unreportednot detected.
Algae, powder or groundGarcía-Salgado et al. 2012Laminaria (Laminaria digitata), FranceCollection date unreportednot detected.
10 findings · 4 studies
Algae, as soldWHO GEMS/FoodWPRO2024As sold / freshmedian.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshmean.
Algae, as soldEuropean Food Safety Authority (EFSA) 2023EU occurrence data2011–2021As sold / freshnot detected.
Algae, as soldLin et al. 2021all samples, TaiwanCollection date unreportedAs sold / freshmean.
Algae, as soldLin et al. 2021all samples, TaiwanCollection date unreportedAs sold / freshmean.
Algae, as soldKim et al. 2023all samples in category2021Basis not statedmean.
Algae, as soldKim et al. 2023Sea algae (n = 105)2021Basis not statednot detected.
Algae, as soldKim et al. 2023Sea algae (n = 105)2021Basis not statedmax.
16 findings · 1 study
Algae, driedAlmela et al. 2002all 18 productsCollection date unreportedrange.
Algae, driedAlmela et al. 2002retail product 1Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 2Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 3Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 4Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 5Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 6Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 7Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 8Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 9Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 10Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 11Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 12Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 13Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 14Collection date unreportedsample value.
Algae, driedAlmela et al. 2002retail product 18Collection date unreportedsample value.
3 findings · 2 studies
Algae, as soldLin et al. 2021all samples, TaiwanCollection date unreportedAs sold / freshrange.
Algae, as soldLin et al. 2021all samples, TaiwanCollection date unreportedAs sold / freshrange.
Algae, as soldKim et al. 2023all samples in category2021Basis not statednot detected.
2 findings · 1 study
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2014all samples, EFSA FoodEx subgroup, LB2000–2013As sold / freshmean.
Algae, as soldEFSA Panel on Contaminants in the Food Chain (CONTAM) 2014all samples, EFSA FoodEx subgroup, UB2000–2013As sold / freshmean.
1 finding · 1 study
Algae, as soldWHO GEMS/FoodWPRO2024As sold / freshmedian.
2 findings · 1 study
Algae, powder or groundGarcía-Salgado et al. 2012Fucus (Fucus vesiculosus), FranceCollection date unreportedsample value.
Algae, powder or groundGarcía-Salgado et al. 2012Laminaria (Laminaria digitata), FranceCollection date unreportedsample value.
2 findings · 1 study
Algae, powder or groundGarcía-Salgado et al. 2012Fucus (Fucus vesiculosus), FranceCollection date unreportedsample value.
Algae, powder or groundGarcía-Salgado et al. 2012Laminaria (Laminaria digitata), FranceCollection date unreportedsample value.
2 findings · 1 study
Algae, powder or groundGarcía-Salgado et al. 2012Fucus (Fucus vesiculosus), FranceCollection date unreportedsample value.
Algae, powder or groundGarcía-Salgado et al. 2012Laminaria (Laminaria digitata), FranceCollection date unreportednot detected.
2 findings · 1 study
Algae, powder or groundGarcía-Salgado et al. 2012Fucus (Fucus vesiculosus), FranceCollection date unreportedsample value.
Algae, powder or groundGarcía-Salgado et al. 2012Laminaria (Laminaria digitata), FranceCollection date unreportednot detected.
2 findings · 1 study
Algae, powder or groundGarcía-Salgado et al. 2012Fucus (Fucus vesiculosus), FranceCollection date unreportednot detected.
Algae, powder or groundGarcía-Salgado et al. 2012Laminaria (Laminaria digitata), FranceCollection date unreportednot detected.
2 findings · 1 study
Algae, powder or groundGarcía-Salgado et al. 2012Fucus (Fucus vesiculosus), FranceCollection date unreportedsample value.
Algae, powder or groundGarcía-Salgado et al. 2012Laminaria (Laminaria digitata), FranceCollection date unreportedsample value.
2 findings · 1 study
Algae, powder or groundGarcía-Salgado et al. 2012Fucus (Fucus vesiculosus), FranceCollection date unreportednot detected.
Algae, powder or groundGarcía-Salgado et al. 2012Laminaria (Laminaria digitata), FranceCollection date unreportednot detected.
1 finding · 1 study
Algae, as soldEuropean Food Safety Authority (EFSA) 2023pooled fresh/unprocessed brown algae2011–2021As sold / freshmean.
3 findings · 1 study
Algae, driedEuropean Food Safety Authority (EFSA) 2023Brown algae, unspecified / Dried product2011–2021As sold / freshmean.
Algae, driedEuropean Food Safety Authority (EFSA) 2023pooled dried algae types2011–2021As sold / freshmean.
Algae, driedEuropean Food Safety Authority (EFSA) 2023pooled dried algae types2011–2021As sold / freshmean.
2 findings · 1 study
Algae, powder or groundGarcía-Salgado et al. 2012Fucus (Fucus vesiculosus), FranceCollection date unreportednot detected.
Algae, powder or groundGarcía-Salgado et al. 2012Laminaria (Laminaria digitata), FranceCollection date unreportednot detected.
2 findings · 1 study
Algae, powder or groundGarcía-Salgado et al. 2012Fucus (Fucus vesiculosus), FranceCollection date unreportednot detected.
Algae, powder or groundGarcía-Salgado et al. 2012Laminaria (Laminaria digitata), FranceCollection date unreportednot detected.
2 findings · 1 study
Algae, powder or groundGarcía-Salgado et al. 2012Fucus (Fucus vesiculosus), FranceCollection date unreportedsample value.
Algae, powder or groundGarcía-Salgado et al. 2012Laminaria (Laminaria digitata), FranceCollection date unreportedsample value.
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 algae Pb reference · Algae, as sold

Reference and scope

HMI algae Pb reference · Algae, as sold. Algae, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference≤50≤50≤50
Alternative weighting≤50≤50≤50

1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
WHO GEMS/Food1100%

Methods

HMI pools subgroup medians for algae, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

WHO GEMS/Food is the only compatible sampling family for algae, as sold on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-8a2c9cb95185:adad3edc2ee4

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae Pb reference · Algae, as sold, dry weight

Reference and scope

HMI algae Pb reference · Algae, as sold, dry weight. Algae, as sold; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference≤15≤15≤15
Alternative weighting≤15≤15≤15

1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
WHO GEMS/Food1100%

Methods

HMI pools subgroup medians for algae, as sold on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

WHO GEMS/Food is the only compatible sampling family for algae, as sold on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-e331d2b7d11b:98bb7b45c401

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae Pb reference · Algae, dried, dry weight

Reference and scope

HMI algae Pb reference · Algae, dried, dry weight. Algae, dried; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference190300930
Alternative weighting190300930

10 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
Almela et al. 200210100%

Methods

HMI pools subgroup medians for algae, dried on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

Almela et al. 2002 is the only compatible sampling family for algae, dried on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-2d021944b2d4:f542ddc13dbe

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae Cd reference · Algae, as sold

Reference and scope

HMI algae Cd reference · Algae, as sold. Algae, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference404040
Alternative weighting404040

1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
WHO GEMS/Food1100%

Methods

HMI pools subgroup medians for algae, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

WHO GEMS/Food is the only compatible sampling family for algae, as sold on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-e3517c703d1b:d0bd66cfd907

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae Cd reference · Algae, dried, dry weight

Reference and scope

HMI algae Cd reference · Algae, dried, dry weight. Algae, dried; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference170380750
Alternative weighting170380750

15 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
Almela et al. 200215100%

Methods

HMI pools subgroup medians for algae, dried on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

Almela et al. 2002 is the only compatible sampling family for algae, dried on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-2e813469d58c:28f7bc92cc5b

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae tAs reference · Algae, as sold

Reference and scope

HMI algae tAs reference · Algae, as sold. Algae, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference2950905017300
Alternative weighting66701090020500

16 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
WHO GEMS/Food16100%

Methods

HMI pools subgroup medians for algae, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

WHO GEMS/Food is the only compatible sampling family for algae, as sold on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-fcf7f66ccca6:a0c40e8d4969

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae tAs reference · Algae, as sold, dry weight

Reference and scope

HMI algae tAs reference · Algae, as sold, dry weight. Algae, as sold; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference135003220043700
Alternative weighting135003220043700

4 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
WHO GEMS/Food250%
EFSA Panel on Contaminants in the Food Chain (CONTAM) 2009250%

Methods

HMI pools subgroup medians for algae, as sold on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

2 sampling families with different designs; none is a probability sample of world supply. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-0d5cdfba4f60:7d3c508c86cf

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae tAs reference · Algae, dried, dry weight

Reference and scope

HMI algae tAs reference · Algae, dried, dry weight. Algae, dried; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference237003000042000
Alternative weighting237003000042000

15 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
Almela et al. 200215100%

Methods

HMI pools subgroup medians for algae, dried on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

Almela et al. 2002 is the only compatible sampling family for algae, dried on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-49cf3e1f4c51:ed4735de6995

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae tAs reference · Algae, powder or ground, dry weight

Reference and scope

HMI algae tAs reference · Algae, powder or ground, dry weight. Algae, powder or ground; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference4700086500126000
Alternative weighting4700086500126000

2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
García-Salgado et al. 20122100%

Methods

HMI pools subgroup medians for algae, powder or ground on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

García-Salgado et al. 2012 is the only compatible sampling family for algae, powder or ground on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-c271aba27694:0c9bdc5a453d

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae tAs reference · Algae, flour or meal

Reference and scope

HMI algae tAs reference · Algae, flour or meal. Algae, flour or meal; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference236000236000236000
Alternative weighting236000236000236000

1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
EFSA Panel on Contaminants in the Food Chain (CONTAM) 20091100%

Methods

HMI pools subgroup medians for algae, flour or meal on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

EFSA Panel on Contaminants in the Food Chain (CONTAM) 2009 is the only compatible sampling family for algae, flour or meal on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-9a2e86762c76:223d5c0434ec

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae iAs reference · Algae, as sold

Reference and scope

HMI algae iAs reference · Algae, as sold. Algae, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference17.5–70 (bounded)100–110 (bounded)186–200 (bounded)
Alternative weighting15.5–70 (bounded)85–110 (bounded)186–211 (bounded)

27 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
WHO GEMS/Food27100%

Methods

HMI pools subgroup medians for algae, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

WHO GEMS/Food is the only compatible sampling family for algae, as sold on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-19b1f31b2307:f413b9aee6b5

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae iAs reference · Algae, dried, dry weight

Reference and scope

HMI algae iAs reference · Algae, dried, dry weight. Algae, dried; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference180260370
Alternative weighting180260370

15 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
Almela et al. 200215100%

Methods

HMI pools subgroup medians for algae, dried on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

Almela et al. 2002 is the only compatible sampling family for algae, dried on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-8b518fa6a958:d99950ac62dd

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae iAs reference · Algae, powder or ground, dry weight

Reference and scope

HMI algae iAs reference · Algae, powder or ground, dry weight. Algae, powder or ground; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference110004400077000
Alternative weighting110004400077000

2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
García-Salgado et al. 20122100%

Methods

HMI pools subgroup medians for algae, powder or ground on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

García-Salgado et al. 2012 is the only compatible sampling family for algae, powder or ground on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-743f864b826d:7208b2b1493c

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae DMA reference · Algae, as sold

Reference and scope

HMI algae DMA reference · Algae, as sold. Algae, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference450485520
Alternative weighting450485520

2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
WHO GEMS/Food2100%

Methods

HMI pools subgroup medians for algae, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

WHO GEMS/Food is the only compatible sampling family for algae, as sold on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-01922cea89bf:d1aca9a2177c

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae DMA reference · Algae, as sold, dry weight

Reference and scope

HMI algae DMA reference · Algae, as sold, dry weight. Algae, as sold; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference684684684
Alternative weighting684684684

1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
WHO GEMS/Food1100%

Methods

HMI pools subgroup medians for algae, as sold on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

WHO GEMS/Food is the only compatible sampling family for algae, as sold on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-9834c5701519:cbcf21e0a698

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae DMA reference · Algae, powder or ground, dry weight

Reference and scope

HMI algae DMA reference · Algae, powder or ground, dry weight. Algae, powder or ground; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference550550550
Alternative weighting550550550

1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
García-Salgado et al. 20121100%

Methods

HMI pools subgroup medians for algae, powder or ground on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

García-Salgado et al. 2012 is the only compatible sampling family for algae, powder or ground on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-78956e373425:778b42df727c

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae MMA reference · Algae, powder or ground, dry weight

Reference and scope

HMI algae MMA reference · Algae, powder or ground, dry weight. Algae, powder or ground; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference≤27≤27≤27
Alternative weighting≤27≤27≤27

2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
García-Salgado et al. 20122100%

Methods

HMI pools subgroup medians for algae, powder or ground on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

García-Salgado et al. 2012 is the only compatible sampling family for algae, powder or ground on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-3f9f36f9659d:66027b0656d4

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae tHg reference · Algae, as sold

Reference and scope

HMI algae tHg reference · Algae, as sold. Algae, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference≤50≤50≤50
Alternative weighting≤50≤50≤50

1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
WHO GEMS/Food1100%

Methods

HMI pools subgroup medians for algae, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

WHO GEMS/Food is the only compatible sampling family for algae, as sold on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-f0b2a74eee79:0b45343d2685

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae tHg reference · Algae, dried, dry weight

Reference and scope

HMI algae tHg reference · Algae, dried, dry weight. Algae, dried; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference1220.633.6
Alternative weighting1220.633.6

15 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
Almela et al. 200215100%

Methods

HMI pools subgroup medians for algae, dried on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

Almela et al. 2002 is the only compatible sampling family for algae, dried on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-e9b8262ada72:2cc3e586ad83

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae Al reference · Algae, as sold

Reference and scope

HMI algae Al reference · Algae, as sold. Algae, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference370037003700
Alternative weighting370037003700

1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
WHO GEMS/Food1100%

Methods

HMI pools subgroup medians for algae, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

WHO GEMS/Food is the only compatible sampling family for algae, as sold on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-1f8a0934a263:1b841b66bcea

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae arsenosugar (glycerol sugar) reference · Algae, powder or ground, dry weight

Reference and scope

HMI algae arsenosugar (glycerol sugar) reference · Algae, powder or ground, dry weight. Algae, powder or ground; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference2600640010200
Alternative weighting2600640010200

2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
García-Salgado et al. 20122100%

Methods

HMI pools subgroup medians for algae, powder or ground on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

García-Salgado et al. 2012 is the only compatible sampling family for algae, powder or ground on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-5ba5ca5ae5c6:9105cca49435

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae arsenosugar (phosphate sugar) reference · Algae, powder or ground, dry weight

Reference and scope

HMI algae arsenosugar (phosphate sugar) reference · Algae, powder or ground, dry weight. Algae, powder or ground; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference80021503500
Alternative weighting80021503500

2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
García-Salgado et al. 20122100%

Methods

HMI pools subgroup medians for algae, powder or ground on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

García-Salgado et al. 2012 is the only compatible sampling family for algae, powder or ground on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-47f63c8aecc6:43e521bf9d9e

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae arsenosugar (sulfate sugar) reference · Algae, powder or ground, dry weight

Reference and scope

HMI algae arsenosugar (sulfate sugar) reference · Algae, powder or ground, dry weight. Algae, powder or ground; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference≤763600–3640 (bounded)7200
Alternative weighting≤763600–3640 (bounded)7200

2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
García-Salgado et al. 20122100%

Methods

HMI pools subgroup medians for algae, powder or ground on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

García-Salgado et al. 2012 is the only compatible sampling family for algae, powder or ground on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-b001469d9e28:3deed5c41fd1

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae arsenosugar (sulfonate sugar) reference · Algae, powder or ground, dry weight

Reference and scope

HMI algae arsenosugar (sulfonate sugar) reference · Algae, powder or ground, dry weight. Algae, powder or ground; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference≤62300–331 (bounded)600
Alternative weighting≤62300–331 (bounded)600

2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
García-Salgado et al. 20122100%

Methods

HMI pools subgroup medians for algae, powder or ground on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

García-Salgado et al. 2012 is the only compatible sampling family for algae, powder or ground on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-b74236cb9e6d:0218ccd684cf

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae As(III) reference · Algae, powder or ground, dry weight

Reference and scope

HMI algae As(III) reference · Algae, powder or ground, dry weight. Algae, powder or ground; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference≤19≤19≤19
Alternative weighting≤19≤19≤19

2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
García-Salgado et al. 20122100%

Methods

HMI pools subgroup medians for algae, powder or ground on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

García-Salgado et al. 2012 is the only compatible sampling family for algae, powder or ground on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-58d4e294642d:3733c8d5937f

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae As(V) reference · Algae, powder or ground, dry weight

Reference and scope

HMI algae As(V) reference · Algae, powder or ground, dry weight. Algae, powder or ground; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference110004400077000
Alternative weighting110004400077000

2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
García-Salgado et al. 20122100%

Methods

HMI pools subgroup medians for algae, powder or ground on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

García-Salgado et al. 2012 is the only compatible sampling family for algae, powder or ground on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-79720a3c3ddd:68e21c0db6be

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae AsB reference · Algae, powder or ground, dry weight

Reference and scope

HMI algae AsB reference · Algae, powder or ground, dry weight. Algae, powder or ground; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference≤33≤33≤33
Alternative weighting≤33≤33≤33

2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
García-Salgado et al. 20122100%

Methods

HMI pools subgroup medians for algae, powder or ground on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

García-Salgado et al. 2012 is the only compatible sampling family for algae, powder or ground on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-697715c800d8:09151095f1e3

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae TETRA reference · Algae, powder or ground, dry weight

Reference and scope

HMI algae TETRA reference · Algae, powder or ground, dry weight. Algae, powder or ground; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference≤67≤67≤67
Alternative weighting≤67≤67≤67

2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
García-Salgado et al. 20122100%

Methods

HMI pools subgroup medians for algae, powder or ground on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

García-Salgado et al. 2012 is the only compatible sampling family for algae, powder or ground on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-34b771bde32e:5b0862b014fa

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae TMAO reference · Algae, powder or ground, dry weight

Reference and scope

HMI algae TMAO reference · Algae, powder or ground, dry weight. Algae, powder or ground; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference≤64≤64≤64
Alternative weighting≤64≤64≤64

2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
García-Salgado et al. 20122100%

Methods

HMI pools subgroup medians for algae, powder or ground on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

García-Salgado et al. 2012 is the only compatible sampling family for algae, powder or ground on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-eed192b56bd5:000b11a335a7

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

HMI algae water-extractable As reference · Algae, powder or ground, dry weight

Reference and scope

HMI algae water-extractable As reference · Algae, powder or ground, dry weight. Algae, powder or ground; Dry weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.

Reference (µg/kg)Q1MedianQ3
Primary HMI reference360006400092000
Alternative weighting360006400092000

2 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.

Contributing familyReference unitsWeight
García-Salgado et al. 20122100%

Methods

HMI pools subgroup medians for algae, powder or ground on a dry weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.

Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.

Limitations

García-Salgado et al. 2012 is the only compatible sampling family for algae, powder or ground on this basis in the completed algae ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.

Admitted source families

Reference version and interpretation

Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.

hmi-pooled-reference-v2:algae-f64881070243:ccbdf3c2a45e

The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.

1 dataset

How metals reach algae

No study in the library compared algae from contaminated and ordinary settings, so the routes by which metals reach it are not measured here.

Which forms and regions measured lower

For total arsenic, the HMI reference median was lowest for algae, as sold (9,050 µg/kg) and highest for algae, as sold (32,200 µg/kg); forms differ in water content, so this compares foods as sold or eaten, not uptake.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →8EFSA Panel on Contaminants in the Food Chain (CONTAM) · 2009Scientific Opinion on Arsenic in FoodEFSA Journal 2009;7(10):1351Read source → The HMI reference for lead in algae, dried pools 10 subgroup units from 1 sampling family, with a median of 300 µg/kg and a middle half spanning 190 (lower quartile) and 930 µg/kg (upper quartile).9Almela C, Algora S, Benito V, Clemente MJ, Devesa V, Súñer MA, Vélez D, Montoro R · 2002Heavy Metal, Total Arsenic, and Inorganic Arsenic Contents of Algae Food ProductsJournal of Agricultural and Food ChemistryRead source → For cadmium in algae, dried, the reference median was 380 µg/kg, with a middle half from 170 to 750 µg/kg across 15 units.9Almela C, Algora S, Benito V, Clemente MJ, Devesa V, Súñer MA, Vélez D, Montoro R · 2002Heavy Metal, Total Arsenic, and Inorganic Arsenic Contents of Algae Food ProductsJournal of Agricultural and Food ChemistryRead source → For total arsenic in algae, as sold, the reference median was 32,200 µg/kg, with a middle half from 13,500 to 43,700 µg/kg across 4 units.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →8EFSA Panel on Contaminants in the Food Chain (CONTAM) · 2009Scientific Opinion on Arsenic in FoodEFSA Journal 2009;7(10):1351Read source →

Among GEMS/Food reporting regions, algae, as sold had the lowest total arsenic subgroup median in WPRO (890 µg/kg) and the highest in EURO (41,800 µg/kg); reporting regions are markets, not growing areas.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → For inorganic arsenic, the lowest regional median was in WPRO (60 µg/kg) and the highest in PAHO (637 µg/kg).1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →

In one study, lead across 10 groups of algae ranged from 150 µg/kg (retail product 7) to 1,330 µg/kg (retail product 1); the lowest is the lowest observed in that study, not an established sourcing preference.9Almela C, Algora S, Benito V, Clemente MJ, Devesa V, Súñer MA, Vélez D, Montoro R · 2002Heavy Metal, Total Arsenic, and Inorganic Arsenic Contents of Algae Food ProductsJournal of Agricultural and Food ChemistryRead source →

Processing, cooking and preparation

No processing study for metals in this food is in the library yet.

Mitigation for algae

Lot testing against the applicable limit is the check that can be verified.

No measured way to lower metals in this food is in the library yet.

Trade-offs and limits of controls

Metals do not move together, so a lot that passes a lead limit says little about cadmium, arsenic or nickel unless those are tested as well.

Testing algae for metals

Results depend on the method and its reporting limit. Reporting limits for lead ranged from 1 µg/kg (Kim et al. 2023) to 50 µg/kg (WHO GEMS/Food), so a non-detect from a less sensitive method says much less.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →5Kim DY, Jeon H, Shin HS · 2023Risk Assessment and Determination of Arsenic and Heavy Metals in Fishery Products in KoreaFoodsRead source → Reporting limits for cadmium ranged from 1 µg/kg (Kim et al. 2023) to 40 µg/kg (WHO GEMS/Food), so a non-detect from a less sensitive method says much less.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →5Kim DY, Jeon H, Shin HS · 2023Risk Assessment and Determination of Arsenic and Heavy Metals in Fishery Products in KoreaFoodsRead source → Reporting limits for total arsenic ranged from 1 µg/kg (WHO GEMS/Food) to 398 µg/kg (WHO GEMS/Food), so a non-detect from a less sensitive method says much less.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →

A useful lot result names the form, the basis and a quantification limit well below the limit that applies.

Buying and verifying algae

No maximum level for metals in algae was verified from primary text for this page; buyers should confirm the limit that applies in the destination market.

Exposure from algae

No source in the library converted algae concentrations into a verified estimate of intake for a defined population. Concentrations describe the food, not individual risk.

Evidence review and remaining gaps

Every source record that names algae was decided on its content: 14 occurrence extracted, 14 records in all. The occurrence table renders every extracted result; held values remain visible with their reason.

References identify the sources used in these answers. The Sources index preserves additional discovery links; inclusion there does not mean a source has been reviewed for this assessment. Corrections, completed searches, new direct evidence and changes in requirements should reopen the relevant answer.

Algae FAQs

What heavy metals are found in algae?

The library reports lead, cadmium, total arsenic, inorganic arsenic, dimethylarsinic acid, monomethylarsonic acid, total mercury, methylmercury, chromium, aluminium, arsenosugar (glycerol sugar), arsenosugar (phosphate sugar), arsenosugar (sulfate sugar), arsenosugar (sulfonate sugar), As(III), As(V), AsB, I, TETRA, TMAO and water-extractable As in algae, most often lead, cadmium and total arsenic.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2European Food Safety Authority (EFSA), Dujardin B, Ferreira de Sousa R, Gomez Ruiz JA · 2023Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →3Fechner C, Hackethal C, Höpfner T, Dietrich J, Bloch D, Lindtner O, Sarvan I · 2022Results 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 →4EFSA Panel on Contaminants in the Food Chain (CONTAM) · 2010Scientific Opinion on Lead in FoodEFSA Journal 2010;8(4):1570Read source → WHO GEMS/Food submissions reported lead in algae, as sold from 18 results in 2 reporting regions, with subgroup medians below 50 µg/kg, mostly non-detects.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →

Which types of algae have the lowest levels?

For total arsenic, the HMI reference median was lowest for algae, as sold (9,050 µg/kg) and highest for algae, as sold (32,200 µg/kg); forms differ in water content, so this compares foods as sold or eaten, not uptake.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →8EFSA Panel on Contaminants in the Food Chain (CONTAM) · 2009Scientific Opinion on Arsenic in FoodEFSA Journal 2009;7(10):1351Read source →

Which regions report the lowest levels in algae?

Among GEMS/Food reporting regions, algae, as sold had the lowest total arsenic subgroup median in WPRO (890 µg/kg) and the highest in EURO (41,800 µg/kg); reporting regions are markets, not growing areas.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → For inorganic arsenic, the lowest regional median was in WPRO (60 µg/kg) and the highest in PAHO (637 µg/kg).1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →

How much of the arsenic in algae is inorganic?

Inorganic arsenic, the more toxic form, was measured in 32 results from 6 sources, far fewer than total arsenic.1World Health Organization · 2026GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2European Food Safety Authority (EFSA), Dujardin B, Ferreira de Sousa R, Gomez Ruiz JA · 2023Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead source →10European Food Safety Authority (EFSA) · 2014Dietary exposure to inorganic arsenic in the European populationEFSA Journal 2014;12(3):3597Read source →9Almela C, Algora S, Benito V, Clemente MJ, Devesa V, Súñer MA, Vélez D, Montoro R · 2002Heavy Metal, Total Arsenic, and Inorganic Arsenic Contents of Algae Food ProductsJournal of Agricultural and Food ChemistryRead source →11Díaz O, Tapia Y, Muñoz O, Montoro R, Velez D, Almela C · 2012Total and inorganic arsenic concentrations in different species of economically important algae harvested from coastal zones of ChileFood and Chemical ToxicologyRead source →12García-Salgado S, Quijano MA, Bonilla MM · 2012Arsenic speciation in edible alga samples by microwave-assisted extraction and high performance liquid chromatography coupled to atomic fluorescence spectrometryAnalytica Chimica ActaRead source → European Food Safety Authority (EFSA) 2023 reported inorganic arsenic at 241 µg/kg (mean) in algae, as sold from EU occurrence data.2European Food Safety Authority (EFSA), Dujardin B, Ferreira de Sousa R, Gomez Ruiz JA · 2023Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEFSA JournalRead 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.

  1. GEMS/Food Contaminants database heavy-metal exportsWorld Health Organization · GEMS/Food Contamination Monitoring and Assessment Programme · 2026 · extranet.who.intDataset
  2. Dietary exposure to heavy metals and iodine intake via consumption of seaweeds and halophytes in the European populationEuropean Food Safety Authority (EFSA), Dujardin B, Ferreira de Sousa R, and Gomez Ruiz JA · EFSA Journal · 2023 · doi.org/10.2903/j.efsa.2023.7798Peer-reviewed
  3. 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 foodsFechner C, Hackethal C, Höpfner T, Dietrich J, Bloch D, Lindtner O, et al. · Food Chemistry: X · 2022 · doi.org/10.1016/j.fochx.2022.100326Peer-reviewed
  4. Scientific Opinion on Lead in FoodEFSA Panel on Contaminants in the Food Chain (CONTAM) · EFSA Journal 2010;8(4):1570 · 2010 · doi.org/10.2903/j.efsa.2010.1570Government
  5. Risk Assessment and Determination of Arsenic and Heavy Metals in Fishery Products in KoreaKim DY, Jeon H, and Shin HS · Foods · 2023 · doi.org/10.3390/foods12203750Peer-reviewed
  6. Dietary Lead Exposure and Associated Health Risks in Guangzhou, ChinaWang M, Liang B, Zhang W, Chen K, Zhang Y, Zhou H, et al. · International Journal of Environmental Research and Public Health · 2019 · doi.org/10.3390/ijerph16081417Peer-reviewed
  7. Dietary Exposure of the Taiwan Population to Mercury Content in Various Seafood Assessed by a Total Diet StudyLin P, Nan FH, and Ling MP · International Journal of Environmental Research and Public Health · 2021 · doi.org/10.3390/ijerph182212227Peer-reviewed
  8. Scientific Opinion on Arsenic in FoodEFSA Panel on Contaminants in the Food Chain (CONTAM) · EFSA Journal 2009;7(10):1351 · 2009 · doi.org/10.2903/j.efsa.2009.1351Government
  9. Heavy Metal, Total Arsenic, and Inorganic Arsenic Contents of Algae Food ProductsAlmela C, Algora S, Benito V, Clemente MJ, Devesa V, Súñer MA, et al. · Journal of Agricultural and Food Chemistry · 2002 · doi.org/10.1021/jf0110250Peer-reviewed
  10. Dietary exposure to inorganic arsenic in the European populationEuropean Food Safety Authority (EFSA) · EFSA Journal 2014;12(3):3597 · 2014 · doi.org/10.2903/j.efsa.2014.3597Government
  11. Total and inorganic arsenic concentrations in different species of economically important algae harvested from coastal zones of ChileDíaz O, Tapia Y, Muñoz O, Montoro R, Velez D, and Almela C · Food and Chemical Toxicology · 2012 · doi.org/10.1016/j.fct.2011.11.024Peer-reviewed
  12. Arsenic speciation in edible alga samples by microwave-assisted extraction and high performance liquid chromatography coupled to atomic fluorescence spectrometryGarcía-Salgado S, Quijano MA, and Bonilla MM · Analytica Chimica Acta · 2012 · doi.org/10.1016/j.aca.2011.12.001Peer-reviewed

Sources

Browse Algae 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 algae record in the library: 14 occurrence sources, references by form and basis, same-study contrasts.