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; arsenic (As)/lead (Pb)/cadmium (Cd) in mg/kg dw, mercury (Hg) in µg/kg dw):
| Type | Species | Product | total As | inorganic As | Pb | Cd | Hg (µg/kg) |
|---|---|---|---|---|---|---|---|
| green | Enteromorpha sp. | green nori flakes | 2.3 ± 0.1 | 0.37 ± 0.07 | 1.33 ± 0.03 | 0.03 ± 0.01 | 20.6 ± 0.4 |
| green | Ulva pertusa | AO nori | 5.17 ± 0.05 | 0.36 ± 0.06 | 0.93 ± 0.02 | 0.17 ± 0.01 | 18 ± 2 |
| red | Porphyra tenera | nori | 23.7 ± 0.5 | 0.57 ± 0.04 | 0.31 ± 0.06 | 0.35 ± 0.01 | 14 ± 2 |
| red | Porphyra tenera | nori | 28.3 ± 0.5 | 0.19 ± 0.02 | 0.289 ± 0.004 | 0.18 ± 0.02 | 4 ± 1 |
| red | Porphyra tenera | toasted nori | 30 ± 1 | 0.314 ± 0.005 | 0.29 ± 0.02 | 0.38 ± 0.01 | 11.3 ± 0.4 |
| red | Palmaria palmata | Atlantic dulse | 7.56 ± 0.02 | 0.44 ± 0.06 | 1.1 ± 0.2 | 0.70 ± 0.03 | 10.5 ± 0.4 |
| brown | Eisenia bicyclis | ise wild arame | 23.8 ± 0.5 | 0.17 ± 0.02 | 0.15 ± 0.08 | 0.75 ± 0.01 | 33.6 ± 0.2 |
| brown | Eisenia bicyclis | ise wild arame | 29 ± 1 | 0.185 ± 0.005 | 0.18 ± 0.01 | 0.67 ± 0.03 | 42 ± 3 |
| brown | Eisenia bicyclis | arame | 30.0 ± 0.1 | 0.15 ± 0.06 | 0.19 ± 0.02 | 0.74 ± 0.02 | 38 ± 3 |
| brown | Undaria pinnatifida | wakame | 32 ± 1 | 0.15 ± 0.10 | <LOD | 1.5 ± 0.1 | 12 ± 1 |
| brown | Undaria pinnatifida | wakame | 42 ± 2 | 0.26 ± 0.03 | <LOD | 0.13 ± 0.03 | 23 ± 3 |
| brown | Undaria pinnatifida | Japanese wakame | 34.6 ± 0.3 | 0.18 ± 0.05 | <LOD | 1.9 ± 0.1 | 14 ± 1 |
| brown | Laminaria japonica | Japanese kombu | 47 ± 1 | 0.297 ± 0.001 | <LOD | 0.15 ± 0.02 | 30 ± 5 |
| brown | Laminaria japonica | kombu | 53 ± 1 | 0.254 ± 0.005 | <LOD | 0.30 ± 0.02 | 37 ± 4 |
| brown | Fucus vesiculosus | alga fucus | 50.0 ± 0.3 | 0.34 ± 0.04 | 0.51 ± 0.04 | 0.55 ± 0.01 | 36 ± 6 |
| brown | Hizikia fusiforme | iziki | 128 ± 5 | 88 ± 6 | 0.63 ± 0.08 | 1.45 ± 0.14 | 35 ± 3 |
| brown | Hizikia fusiforme | hijiki | 141 ± 6 | 85 ± 6 | 0.89 ± 0.15 | 1.46 ± 0.02 | 25.9 ± 0.2 |
| brown | Hizikia fusiforme | Japanese hijiki | 115 ± 12 | 83 ± 5 | 0.53 ± 0.06 | 1.0 ± 0.1 | 30.32 ± 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% inorganic arsenic (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/total arsenic (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.
Update history
The five most recent substantive edits to this page, classified major (evidence or structure moved), correction (a published value or statement was wrong and has been fixed), or minor (narrative rewritten without changing the underlying evidence). Each description is derived from what the edit did to this page; the linked commit is the authoritative record, routine regeneration passes are excluded, and the full version history lives in git.
| Commit | Date | Change | Description |
|---|---|---|---|
| b01ec52c31 | 2026-08-04 | major | 1 section added |
| 3171d069e3 | 2026-08-02 | major | 1 section added |
| 90a2f9a38e | 2026-07-30 | major | 1 section added and 1 removed |
| eaa8eeeedf | 2026-07-27 | major | 1 section added and 1 removed |
| aca5e2155a | 2026-06-09 | major | 1 section added |
