Overview
Ma and colleagues reviewed published total arsenic and inorganic arsenic measurements in seaweeds, grouping the literature by Rhodophyta, Phaeophyta, and Chlorophyta. This is secondary evidence: it compiles prior studies and does not add new sample measurements. The values below are useful for seaweed/kelp food and algae/seaweed supplement context, but downstream occurrence pooling should trace and de-duplicate the underlying primary studies.
Key numbers
All concentration values below are reported by the review as mg kg-1 DW; no unit conversion was performed. The review states that records were collected from published studies available up to June 2017 and that the same seaweed species collected from different geographic zones was treated as a different datum.
Table 1 summary by phylum:
| Phylum | tAs range | tAs average | iAs range | iAs average | iAs/tAs range | iAs/tAs average |
|---|---|---|---|---|---|---|
| Rhodophyta | 0.13~50 | 13.71±9.79 (n=92) | 0.048~3.0 | 0.36±0.32 (n=44) | 0.2~61.54% | 5.97±12.71% (n=44) |
| Phaeophyta | 1.89~245.19 | 50.36±44.60 (n=154) | 0.04~115.56 | 16.65±29.32 (n=65) | 0.08~85.29% | 21.59±28.54% (n=65) |
| Chlorophyta | 0.59~28.53 | 5.59±5.08 (n=36) | 0.02~0.40 | 0.20±0.13 (n=14) | 0.48~16.09% | 5.28±5.78% (n=14) |
The abstract and Section 3 report that total arsenic (tAs) in the top 10 Phaeophyta species is over 100 mg kg-1 DW, while the top 7 Rhodophyta species range from 20 to 50 mg kg-1 DW and the top 3 Chlorophyta species range from 10 to 15 mg kg-1 DW. Section 3.2 reports that Phaeophyta inorganic arsenic (iAs) is significantly higher than Rhodophyta and Chlorophyta (P<0.05), while Rhodophyta and Chlorophyta do not differ significantly (P>0.5).
Table 2 high-tAs species:
| Species | Phylum | Zone | tAs | Method | Reference in review |
|---|---|---|---|---|---|
| Laminaria ochroleuca | Phaeophyta | Spain | 245.19±88.38 | AFS | García-Sartal et al. 2010 |
| Cystoseira barbata | Phaeophyta | Italy | 242 ± 104 | ICP-MS | Caliceti et al. 2002 |
| Sargassum piluliferum | Phaeophyta | Japan | 181±4 | ICP-MS | Karthikeyan & Hirata 2004 |
| S. piluliferum | Phaeophyta | Japan | 181±4 | HPLC-ICP-MS | Hirata & Toshimitsu 2005 |
| Hizikia fusiforme | Phaeophyta | Spain | 141 ±6 | FI-HG-AAS | Almela et al. 2002 |
| H. fusiforme | Phaeophyta | Spain | 103-147 | AAS | Besada et al. 2009 |
| H. fusiforme | Phaeophyta | Japan | 115 ± 12 | FI-HG-AAS | Almela et al. 2002 |
| H. fusiforme | Phaeophyta | Japan | 109.6 ±24.03 | FI-HG-AAS | Almela et al. 2006 |
| Hizikia spp. | Phaeophyta | UK | 108.67±8.82 | ICP-MS | Rose et al. 2007 |
| Fucus vesiculosis | Phaeophyta | UK | 140 | HPLC-ICP-MS | Pedersen & Francesconi 2000 |
| Laminaria spp. | Phaeophyta | Brittany, France | 134 | HPLC-ICP-MS | McSheehy & Szpunar 2000 |
| L. digitata | Phaeophyta | France | 126±5 | HPLC-ICP-MS | García-Sartal et al. 2012 |
| L. digitata | Phaeophyta | USA | 106.73 | ICP-MS | Taylor & Jackson 2016 |
| Cystoseira barbata | Phaeophyta | Syria | 131 ± 1 | GS | Al-Masri et al. 2003 |
| Melanosiphen intestinalis | Phaeophyta | Japan | 119.6±1.6 | HPLC-ICP-MS | Hirata & Toshimitsu 2005 |
| Porphyra spp. | Rhodophyta | China | 50.0±11.73 | FI-HG-AAS | Almela et al. 2006 |
| P. umbilicales | Rhodophyta | Spain | 28.9-49.5 | AAS | Besada et al. 2009 |
| P. umbilicalis | Rhodophyta | Spain | 34.5 | FI-HG-AAS | Almela et al. 2006 |
| P. umbilicalis | Rhodophyta | Japan | 34±3 | HG-AFS | García-Sartal et al. 2012 |
| Porphyra spp. | Rhodophyta | Japan | 32.7 | FI-HG-AAS | Almela et al. 2006 |
| Porphyra spp. | Rhodophyta | Not known | 30.8 | ICP-MS | Kohlmeyer et al. 2003 |
| P. crispata | Rhodophyta | China | 30.1 ± 1.3 | HPLC-ICP-MS | Van Hulle et al. 2002 |
| Gracilaria gracilis | Rhodophyta | Spain | 32 ± 1 | ICP-MS | Caliceti et al. 2002 |
| Iridaea cordata | Rhodophyta | Antarctic | 28 ± 6 | ICP-OES | Farías et al. 2007 |
| Pyropia endiviifolia | Rhodophyta | Antarctic | 26.0 ± 0.5 | ICP-MS | Picoloto et al. 2017 |
| Chondrus crispus | Rhodophyta | Spain | 23.2-25.5 | AAS | Besada et al. 2009 |
| Codium cuneatum | Chlorophyta | Mexico | 28.53±11.91 | INAA | Sánchez-Rodríguez et al. 2001 |
| Ulva prolifera | Chlorophyta | USA | 14.65 | ICP-MS | Taylor & Jackson 2016 |
| Gayralia oxysperma | Chlorophyta | not reported in extracted table | 12.68 | ICP-MS | Taylor & Jackson 2016 |
| uranium (U). lactuca | Chlorophyta | Norway | 10.33±3.78 | ICP-MS | Duinker 2014 |
The Table 2 footnote defines high-tAs species thresholds as above 100, 20, and 10 mg kg-1 DW for Phaeophyta, Rhodophyta, and Chlorophyta, respectively.
Table 3 high-iAs species:
| Species | Phylum | Zone | iAs | Method | Reference in review |
|---|---|---|---|---|---|
| Sargassum piluliferum | Phaeophyta | Japan | 115.56±7 | ICP-MS | Karthikeyan & Hirata 2004 |
| S. piluliferum | Phaeophyta | Japan | 114.1±2.3 | FI-HG-AAS | Hirata & Toshimitsu 2005 |
| H. fusiforme | Phaeophyta | Spain | 85 ± 6 | FI-HG-AAS | Almela et al. 2002 |
| H. fusiforme | Phaeophyta | Spain | 32.1-69.5 | AAS | Besada et al. 2009 |
| H. fusiforme | Phaeophyta | Japan | 83 ± 5 | FI-HG-AAS | Almela et al. 2002 |
| H. fusiforme | Phaeophyta | Japan | 73.48±23.39 | FI-HG-AAS | Almela et al. 2006 |
| Hizikia spp. | Phaeophyta | UK | 77.44±8.85 | ICP-MS | Rose et al. 2007 |
| Laminaria spp. | Phaeophyta | Brittany | 62 | HPLC-ICP-MS | McSheehy & Szpunar 2000 |
| Melanosiphen intestinalis | Phaeophyta | Japan | 48.78±3.3 | FI-HG-AAS | Hirata & Toshimitsu 2005 |
| Palmaria palmata | Rhodophyta | Brittany | 1.9 | HPLC-ICP-MS | McSheehy & Szpunar 2000 |
| Porphyra umbilicalis | Rhodophyta | Brittany | 3 | HPLC-ICP-MS | McSheehy & Szpunar 2000 |
| Ulva rigida | Chlorophyta | Chile | 0.40 ± 0.29 | FI-HG-AAS | Díaz et al. 2012 |
| Enteromorpha spp. | Chlorophyta | Spain | 0.37 ± 0.07 | FI-HG-AAS | Almela et al. 2002 |
| uranium (U). pertusa | Chlorophyta | Spain | 0.36 ± 0.06 | FI-HG-AAS | Almela et al. 2002 |
The Table 3 footnote defines high-iAs species thresholds as above 50, 1, and 0.3 mg kg-1 DW for Phaeophyta, Rhodophyta, and Chlorophyta, respectively; the extracted footnote prints AsT in this sentence, but the table title and body are for inorganic arsenic.
Additional source-reported context:
- The review states that typical ocean-water arsenic is
1to3 µg l-1, with an average of1.7 μg l-1. - It states that seaweed tAs levels are approximately
1,000-50,000times higher than ocean water, depending on species. - It reports that most species of Rhodophyta, Phaeophyta, and Chlorophyta have tAs below
30,100, and20 mg kg-1 DW, respectively. - It cites one Sargassum sinicola case near Gulf of California hydrothermal venting as above
600 mg kg-1; this is environmental context from a cited study, not a Table 1-3 occurrence summary row. - It reports that arsenosugars make up
>85%of soluble arsenic in most species, citing Rose et al. 2007 and Kalia and Khambholja 2015.
Methods (brief)
This is a peer-reviewed literature review, not a primary measurement study. The authors compiled published seaweed arsenic studies available up to June 2017, summarized total and inorganic arsenic by phylum, and listed high-tAs and high-iAs species with the methodology and cited primary reference where available. Samples of the same species from different geographic zones were treated as separate data points so that each species-zone record corresponded to one datum. Analytical methods in the compiled studies include AFS, ICP-MS, HPLC-ICP-MS, FI-HG-AAS, AAS, GS, HG-AFS, ICP-OES, and INAA.
Implications
This source supports seaweed/kelp food and algae/seaweed supplement context by identifying phylum- and species-level patterns in total arsenic and inorganic arsenic. The review’s most relevant routing signal is that Phaeophyta values, especially hijiki, Sargassum piluliferum, Laminaria spp., and several brown algae, carry much higher secondary-summary iAs than Rhodophyta or Chlorophyta. Because the paper aggregates prior literature and several underlying primary sources are separately ingested in the wiki, these values should not be pooled as independent occurrence measurements without source-level de-duplication.
Related evidence
- Seaweed/kelp foods (nori, wakame, kombu, dulse — as food products)
- Ingredient class — algae/seaweed-based
- Seaweed
- Arsenic, Total
- Arsenic, Inorganic
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; narrative text revised |
| eaa8eeeedf | 2026-07-27 | major | 1 section added |
| 50de6ab217 | 2026-07-27 | minor | Narrative text revised |
