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Heavy Metal Index

Heavy Metal, Total Arsenic, and Inorganic Arsenic Contents of Algae Food Products

Source

Almela and colleagues measured total arsenic, inorganic arsenic, lead, cadmium, and mercury in 18 processed edible-algae food products on retail sale in Spain, using a hydride-generation method for arsenic speciation validated against three macroalgal reference materials.

Page snapshot
Cited by8 pages
Metals measured5
Evidence tierA
Year2002

Overview

Almela and colleagues measured total arsenic, inorganic arsenic, lead, cadmium, and mercury in 18 processed edible-algae food products on retail sale in Spain, using a hydride-generation method for arsenic speciation validated against three macroalgal reference materials. Across the products, total arsenic ranged 2.3–141 mg/kg dry weight and inorganic arsenic 0.15–88 mg/kg dw, with the brown alga Hizikia fusiforme (hijiki) standing apart: its inorganic arsenic (83–88 mg/kg dw) constituted 60–72% of total arsenic, two orders of magnitude above every other product, while 84% of all samples held inorganic arsenic below 1 mg/kg dw. Cadmium reached 1.9 mg/kg dw in wakame and exceeded the French (0.5 mg/kg dw) and Australian (0.2 mg/kg dw) limits in 10 and 14 samples respectively. The study is a foundational speciated-arsenic occurrence survey for the seaweed/kelp food category.

Key numbers

Concentration ranges (mg/kg dry weight unless noted), n=18 products, mean of three independent analyses each:

  • Total arsenic: 2.3–141 mg/kg dw
  • Inorganic arsenic: 0.15–88 mg/kg dw
  • Lead: <0.05 (LOD)–1.33 mg/kg dw
  • Cadmium: 0.03–1.9 mg/kg dw
  • Mercury: 4–42 µg/kg dw (0.004–0.042 mg/kg dw)

Per-product values (Table 3; mean ± SD; As/Pb/Cd in mg/kg dw, Hg in µg/kg dw):

TypeSpeciesProducttotal Asinorganic AsPbCdHg (µg/kg)
greenEnteromorpha sp.green nori flakes2.3 ± 0.10.37 ± 0.071.33 ± 0.030.03 ± 0.0120.6 ± 0.4
greenUlva pertusaAO nori5.17 ± 0.050.36 ± 0.060.93 ± 0.020.17 ± 0.0118 ± 2
redPorphyra teneranori23.7 ± 0.50.57 ± 0.040.31 ± 0.060.35 ± 0.0114 ± 2
redPorphyra teneranori28.3 ± 0.50.19 ± 0.020.289 ± 0.0040.18 ± 0.024 ± 1
redPorphyra teneratoasted nori30 ± 10.314 ± 0.0050.29 ± 0.020.38 ± 0.0111.3 ± 0.4
redPalmaria palmataAtlantic dulse7.56 ± 0.020.44 ± 0.061.1 ± 0.20.70 ± 0.0310.5 ± 0.4
brownEisenia bicyclisise wild arame23.8 ± 0.50.17 ± 0.020.15 ± 0.080.75 ± 0.0133.6 ± 0.2
brownEisenia bicyclisise wild arame29 ± 10.185 ± 0.0050.18 ± 0.010.67 ± 0.0342 ± 3
brownEisenia bicyclisarame30.0 ± 0.10.15 ± 0.060.19 ± 0.020.74 ± 0.0238 ± 3
brownUndaria pinnatifidawakame32 ± 10.15 ± 0.10<LOD1.5 ± 0.112 ± 1
brownUndaria pinnatifidawakame42 ± 20.26 ± 0.03<LOD0.13 ± 0.0323 ± 3
brownUndaria pinnatifidaJapanese wakame34.6 ± 0.30.18 ± 0.05<LOD1.9 ± 0.114 ± 1
brownLaminaria japonicaJapanese kombu47 ± 10.297 ± 0.001<LOD0.15 ± 0.0230 ± 5
brownLaminaria japonicakombu53 ± 10.254 ± 0.005<LOD0.30 ± 0.0237 ± 4
brownFucus vesiculosusalga fucus50.0 ± 0.30.34 ± 0.040.51 ± 0.040.55 ± 0.0136 ± 6
brownHizikia fusiformeiziki128 ± 588 ± 60.63 ± 0.081.45 ± 0.1435 ± 3
brownHizikia fusiformehijiki141 ± 685 ± 60.89 ± 0.151.46 ± 0.0225.9 ± 0.2
brownHizikia fusiformeJapanese hijiki115 ± 1283 ± 50.53 ± 0.061.0 ± 0.130.32 ± 0.03

Additional source-reported facts:

  • In Hizikia fusiforme, inorganic arsenic was 83–88 mg/kg dw, equal to 60–72% of total arsenic in those samples; the authors note literature values of 50–70% iAs in H. fusiforme.
  • 84% of samples had inorganic arsenic <1 mg/kg dw (0.15–0.57 mg/kg dw).
  • The three H. fusiforme samples exceeded the French/US inorganic-arsenic limit (3 mg/kg dw) and the Australia/New Zealand limit (1 mg/kg dw).
  • 10 samples exceeded the French Cd limit (0.5 mg/kg dw); 14 exceeded the Australian limit (0.2 mg/kg dw).
  • Method limits of detection (mg/kg): total As 0.025, inorganic As 0.014, Pb 0.05, Cd 0.003, Hg 0.003.
  • Exposure note: a daily consumption of 1.7 g of H. fusiforme would reach the WHO Provisional Tolerable Weekly Intake for inorganic arsenic (15 µg/kg body weight/week) at 68 kg body weight.

Methods (brief)

Eighteen dried algae food products (12 brown, 4 red, 2 green) bought in Valencia were milled and analyzed in triplicate. Total arsenic and inorganic arsenic were determined by flow-injection hydride-generation atomic absorption spectrometry (FI-HG-AAS); inorganic arsenic [As(III)+As(V)] was isolated beforehand by overnight HCl solubilization followed by chloroform solvent extraction and HCl back-extraction (the Muñoz/Vélez/Montoro seafood method, here assessed for algae). Lead and cadmium were determined by graphite-furnace AAS with Zeeman correction using the standard-additions method after microwave HNO3/H2O2 digestion; mercury by cold-vapor atomic fluorescence spectrometry. Quality control used reference materials Fucus sp. (IAEA), BCR 060 (Lagarosiphon major), and BCR-279 (Ulva lactuca); recoveries for inorganic arsenic spikes were 95–101%. Mercury was reported as total Hg (no speciation); arsenic was speciated to the inorganic fraction. All values are dry weight. The authors note the absence of certified reference materials for inorganic arsenic in this matrix as a limitation.

Implications

  • Certification (HMTc): supplies per-sample speciated inorganic-arsenic, cadmium, and lead occurrence data on the dry-weight, as-sold basis for the Category 6 seaweed-kelp-foods row, where iAs/tAs/Cd are the platform analytes. The data establish a strongly bimodal inorganic-arsenic distribution: most edible algae sit below 1 mg/kg dw iAs, while Hizikia fusiforme (hijiki) is a categorical outlier at >80 mg/kg dw iAs, supporting the within-row species sub-split flagged in the Category 6 Step 0 lock. Cadmium occurrence (up to 1.9 mg/kg dw, exceeding several national algae limits) is independently relevant.
  • App: contributes to the contamination_profile for the seaweed ingredient on inorganic arsenic, total arsenic, cadmium, lead, and total mercury.

Verification notes

  • raw_handle MFK_almela2002 derived from the PDF filename; raw_path is the manual-fetch PDF under “raw/Manual Fetch Kimi /June 8 Inorganic Arsenic Seaweed/“. DOI 10.1021/jf0110250 confirmed on the article header.
  • Evidence tier A: peer-reviewed primary occurrence study with triplicate analysis, validated speciation method, and CRM-based QC.
  • Speciation: arsenic reported as both total As and inorganic As [As(III)+As(V)] — both lifted to frontmatter as tAs and iAs and kept distinct in Key numbers; never collapsed. Mercury reported as total Hg only (CV-AFS, no speciation) → tHg. Chromium and nickel not measured.
  • Units preserved exactly as the source reports: As/Pb/Cd in mg/kg dry weight, Hg in µg/kg dry weight. No conversions applied. Basis is dry weight, as-sold (products sold dried) — recorded in matrices as dry-weight.
  • Brand firewall: not engaged. The source identifies products only by alga species and generic processed-product names (wakame, kombu, nori, yakinori, hijiki, arame, dulse, AO-nori); no commercial brand names appear.
  • Jurisdiction ES (point of retail sale, Valencia). Products are of mixed/Japanese-style origin but the survey samples the Spanish retail market; sampling_locations left empty as the paper gives no harvest geocoordinates.
  • Method vendor/instrument names (Perkin-Elmer AAS, PS Analytical AFS, IAEA/BCR reference materials) retained in Methods as permitted scientific reporting, not brand attribution.
  • matrices [edible-seaweed, macroalgae, kelp, dry-weight] follow established corpus convention (cf. mosusu2023-edible-seaweeds-japan-metals); kelp included because Laminaria japonica (kombu) is present. Kept broad; the routing layer fans to sibling pages.

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