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Wei et al. 2003 - Porphyra arsenosugars from China

Wei and colleagues measured total arsenic and extractable arsenic species in edible Porphyra seaweed from five Chinese locations. The occurrence-relevant table reports dry-weight total arsenic and extractable arsenosugar PO4/OH in market Porphyra; the heating and volunteer urine sections are exposure and metabolism context. The source reports organoarsenic species, not inorganic arsenic, so total arsenic and arsenosugar values should not be substituted for iAs.

Key numbers

Table 3 reports total arsenic, extractable arsenic, and extraction efficiency in Porphyra as mg/kg as arsenic dry weight, mean ± SD with n = 3:

Source areaTotal arsenicExtractable arsenicExtraction efficiency
Dalian4.6 ± 0.6 mg/kg4.1 ± 0.5 mg/kg90%
Qingdao5.8 ± 0.8 mg/kg5.3 ± 0.6 mg/kg92%
Zhejiang8.9 ± 0.3 mg/kg8.3 ± 0.4 mg/kg93%
Fujian2.1 ± 0.1 mg/kg2.0 ± 0.2 mg/kg96%
Guangzhou21.6 ± 1.4 mg/kg20.1 ± 1.2 mg/kg93%

The Results text summarizes the total-arsenic range as 2.1 to 21.6 mg/kg (dry wt), with an average value of 8.6 mg/kg (dry wt) and “standard variance” of 7.7 mg/kg.

Table 4 reports extractable arsenosugar concentrations in mg/kg as arsenic dry weight, mean ± SD with n = 3:

Source areaArsenosugar PO4Arsenosugar OH
Dalian0.3 ± 0.1 mg/kg3.8 ± 0.4 mg/kg
Qingdao4.0 ± 0.4 mg/kg1.3 ± 0.2 mg/kg
Zhejiang5.2 ± 0.3 mg/kg3.1 ± 0.2 mg/kg
Fujian1.3 ± 0.1 mg/kg0.7 ± 0.2 mg/kg
Guangzhou13.9 ± 0.9 mg/kg6.2 ± 0.4 mg/kg

Table 4 peak-abundance context:

Source areaAnion A1Anion A2Cation C2Cation C1
Dalian92.9 ± 1.8%7.1 ± 0.6%92.1 ± 1.9%7.9 ± 0.3%
Qingdao22.2 ± 0.4%77.8 ± 1.6%24.6 ± 0.7%75.4 ± 1.8%
Zhejiang35.6 ± 1.0%64.4 ± 0.9%37.5 ± 0.6%62.5 ± 1.5%
Fujian35.7 ± 0.5%64.3 ± 1.2%36.8 ± 0.1%63.2 ± 1.1%
Guangzhou30.8 ± 0.4%69.2 ± 0.7%31.6 ± 0.3%68.4 ± 1.3%

The authors state that the Porphyra extract peaks did not match inorganic arsenic, MMA, DMA, or AsB standards under their HPLC conditions, and that ES-MS-MS confirmed the two extract species as arsenosugar PO4 and arsenosugar OH. They state that arsenosugars accounted for the complete arsenic content of the Porphyra extract.

Heating and volunteer-metabolism context:

  • Guangzhou Porphyra extract was heated at 100 °C in an oil bath for 10 min; Figure 4 showed no chromatographic difference before versus after heating, and the authors concluded that the arsenosugars remained stable toward short-term heating.
  • Six adult volunteers, five male and one female, refrained from seafood for at least 72 h before consuming 15 g (dry weight) of heated Guangzhou Porphyra in one meal.
  • The ingested Guangzhou Porphyra portion contained ∼324 µg of arsenic as arsenosugars OH and PO4.
  • Urine before ingestion contained total arsenic 10-30 ng/mL; after ingestion, urine arsenic peaked between 18 and 35 h.
  • The 20-30 h urine window gave the highest concentration, 92.5 µg/L, reported as the average value of 19 samples collected during that period.
  • The final urine sample collected after 80 h contained <30 ng/mL.
  • Figure 6/7 HPLC-ICP-MS urine speciation assigned the major post-ingestion peak as DMA; the authors state that the concentration was almost 15-20 times higher than before ingestion.

Quality-control context:

  • For NIST SRM 1571 Orchard Leaves, the certified value was 10 ± 2 mg of As/kg; the study measured 9.5 ± 0.3 mg of As/kg.

Methods (brief)

Chinese seaweeds were collected from Guangzhou, Fujian, Dalian, Qingdao, and Zhejiang in July 2001; three Porphyra samples were bought at local public markets in each location and stored at room temperature before analysis. Total arsenic used 0.5 g subsamples digested with nitric acid and hydrogen peroxide in a microwave oven, then ICP-MS with iridium internal standard. Species extraction rinsed crude seaweed with deionized water, oven-dried samples at 50 °C for 18 h, ground them, extracted 1 g (dry weight) with 20 mL H2O/MeOH (1:1, v/v) by sonication for 15 min and centrifugation, and repeated the extraction twice more. Speciation used anion- and cation-exchange HPLC-ICP-MS, with ES-MS-MS confirmation of arsenosugar identities; urine arsenic species were measured by PRP-X100 anion-exchange HPLC-ICP-MS.

Implications

This paper adds direct seaweed occurrence evidence for Chinese-market Porphyra with dry-weight total arsenic from 2.1 ± 0.1 mg/kg to 21.6 ± 1.4 mg/kg and extractable arsenosugar PO4/OH values reported separately. Its main routing use is the seaweed/kelp food row, but it should not be treated as an inorganic-arsenic source because the extractable species were organoarsenic arsenosugars and no Porphyra iAs concentration was reported. The volunteer data are useful exposure/metabolism context for arsenosugar conversion to urinary DMA, not a product occurrence row.

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Verification notes

  • Identity checks before writing found no existing source page for DOI 10.1021/jf026117j, raw handle MFK_wei2003, title text, author/title text, or cite key wei2003-porphyra-arsenosugars-china.
  • Text was extracted to /tmp/hmi-seaweed-066.txt with pdftotext -layout; the title, abstract, Materials and Methods, Table 3, Table 4, heating section, urine-metabolism section, Figures 4-7 captions, and conclusion were readable.
  • All Key numbers were checked against /tmp/hmi-seaweed-066.txt, especially Table 3 total/extractable arsenic values, Table 4 arsenosugar concentrations and HPLC peak percentages, the 100 °C/10 min heating test, the 15 g (dry weight) ingestion amount, ∼324 µg ingested arsenic, 10-30 ng/mL pre-ingestion urine range, 92.5 µg/L peak-window urine value, and the <30 ng/mL final urine statement.
  • Units and bases are preserved as mg/kg as arsenic dry weight, %, °C, min, g (dry weight), µg, ng/mL, and µg/L; no unit conversion was performed.
  • Speciation check: total arsenic, arsenosugar PO4, arsenosugar OH, DMA in urine, AsB, MMA, arsenite, and arsenate are kept distinct. The paper does not report a Porphyra inorganic-arsenic concentration, so frontmatter uses metals: [tAs] only.
  • Brand firewall: samples were public-market Porphyra by location, not named brands.
  • Missing-slug check: no missing product or ingredient slug blockers. Exact Porphyra and nori/zicai terminology remains in source text while frontmatter routes broadly to seaweed/kelp foods.

Page history

The five most recent substantive edits to this page. The full version history lives in git; when DOI minting comes online (see schema docs), each entry below will also link to a version-pinned DataCite DOI.

CommitDateDescription
4039d202026-06-10scope: broaden ingest to the full upstream+downstream literature (marine, atmospheric, attribution, exposure, toxicology) — inclusion is the default