Shimoda et al. 2010 - commercial hijiki arsenic speciation
Shimoda and colleagues measured total arsenic, water-extracted inorganic arsenic, and arsenosugar species in seven commercially available dried-hijiki products and two raw hijiki samples. The occurrence-relevant matrix is hijiki seaweed on a dry-weight basis, with source-region and production-system context retained from Table 1. Total arsenic, water-extracted total arsenic, inorganic arsenic, DMA, and individual arsenosugar peaks are kept separate below.
Key numbers
Table 1 identifies the nine hijiki samples:
| Sample | Product form | Producing area | Production system |
|---|---|---|---|
| 1 | me-hijiki (sprouts of weed) | China (Hong Kong) | unknown |
| 2 | me-hijiki (sprouts of weed) | South Korea | boiling system |
| 3 | me-hijiki (sprouts of weed) | Mie prefecture (Japan) | boiling system |
| 4 | naga-hijiki (whole of weed) | Ohita prefecture (Japan) | closed-steam system |
| 5 | me-hijiki (sprouts of weed) | Ohita prefecture (Japan) | closed-steam system |
| 6 | naga-hijiki (whole of weed) | Amatsu (Japan) | open-steam system |
| 7 | naga-hijiki (whole of weed) | Kominato (Japan) | open-steam system |
| 8 | raw hijiki (whole of weed) | Amatsu (Japan) | not applicable |
| 9 | raw hijiki (whole of weed) | Kominato (Japan) | not applicable |
Table 4 reports acid-digested total arsenic and water-extracted arsenic fractions in µg As/g dw; each sample solution was measured in triplicate and values are mean ± S.D. (n = 3). No unit conversion was performed.
| Sample | Acid-digested total As (A-TAs) | Water-extracted total As (W-TAs) | Water-extracted iAs (W-iAs) | Water-extracted AsSugs (W-AsS) | W-TAs/A-TAs (%) | W-iAs/A-TAs (%) | W-AsS/A-TAs (%) |
|---|---|---|---|---|---|---|---|
| 1 | 80.9 ± 9.4 | 33.4 ± 2.0 | 27.7 ± 1.7 | 3.0 ± 0.0 | 41.3 | 34.3 | 3.7 |
| 2 | 112.6 ± 1.5 | 65.1 ± 2.7 | 55.8 ± 2.0 | 6.6 ± 0.6 | 57.8 | 49.5 | 5.9 |
| 3 | 86.7 ± 6.7 | 59.0 ± 3.3 | 51.2 ± 2.9 | 5.4 ± 0.3 | 68.0 | 59.0 | 5.9 |
| 4 | 86.3 ± 5.7 | 58.1 ± 1.8 | 51.1 ± 1.5 | 4.4 ± 0.3 | 67.4 | 59.2 | 5.1 |
| 5 | 118.6 ± 11.3 | 81.0 ± 2.6 | 71.3 ± 2.0 | 7.8 ± 0.7 | 68.3 | 60.1 | 6.6 |
| 6 | 37.1 ± 1.2 | 18.4 ± 0.7 | 9.2 ± 0.4 | 8.4 ± 0.4 | 49.5 | 24.8 | 22.7 |
| 7 | 48.7 ± 2.4 | 25.4 ± 1.3 | 13.6 ± 0.5 | 10.9 ± 0.7 | 52.1 | 28.0 | 22.4 |
| 8 | 59.3 ± 8.4 | 32.4 ± 1.2 | 17.4 ± 0.1 | 14.8 ± 1.2 | 54.6 | 29.3 | 24.9 |
| 9 | 72.8 ± 1.8 | 37.7 ± 1.7 | 17.4 ± 0.3 | 20.1 ± 1.5 | 51.8 | 23.9 | 27.6 |
Table 3 reports water-extracted arsenic compounds by HPLC-ICP-MS in µg As/g dw; values are means (n = 3). ND means not detected by HPLC-ICP-MS, and the AsSug 328 peak includes unresolved AsBe and AsSug 254 according to the table footnote.
| Sample | As(III) | DMA | As(V) | AsSug 328 | AsSug 391 | AsSug 392 | AsSug 408 | AsSug 482 | Total AsSugs |
|---|---|---|---|---|---|---|---|---|---|
| 1 | 0.10 | 2.61 | 27.61 | 0.95 | ND | 0.12 | 1.79 | 0.08 | 2.96 |
| 2 | 0.44 | 2.71 | 55.33 | 1.48 | ND | 0.29 | 4.77 | 0.09 | 6.64 |
| 3 | 0.08 | 1.21 | 51.10 | 1.25 | ND | 0.22 | 3.85 | 0.05 | 5.39 |
| 4 | 0.13 | 2.72 | 50.93 | 0.85 | ND | 0.46 | 2.99 | 0.06 | 4.36 |
| 5 | 0.79 | 1.88 | 70.52 | 1.50 | ND | 0.48 | 5.75 | 0.05 | 7.79 |
| 6 | 0.26 | 0.74 | 8.94 | 0.32 | ND | 0.27 | 7.77 | 0.04 | 8.41 |
| 7 | 0.09 | 0.85 | 13.55 | 0.42 | ND | 0.27 | 10.15 | 0.05 | 10.90 |
| 8 | 0.25 | 0.16 | 17.15 | 1.44 | ND | 0.50 | 12.81 | ND | 14.78 |
| 9 | 0.16 | 0.25 | 17.21 | 1.39 | ND | 0.56 | 18.10 | 0.04 | 20.09 |
Source-reported summary statements:
- Acid-digested total arsenic in the nine hijiki samples ranged from
37.1to118.6 µg As/g dw. - Water-extracted total arsenic ranged from
18.4to81.0 µg As/g dw. - The major water-extracted compound was arsenate in all samples (
8.94to70.52 µg As/g dwin Table 3). - Water-extracted arsenosugars represented
3.7to27.6%of acid-digested total arsenic. - AsSug 408 was the major arsenosugar peak in the water extracts.
- The authors state that HPLC-MS/MS detected arsenosugars more sensitively than HPLC-ICP-MS, but HPLC-MS/MS could not detect inorganic arsenic; they therefore recommend combined HPLC-MS/MS and HPLC-ICP-MS for seaweed arsenic-speciation work.
Methods (brief)
Commercial dried-hijiki products and two raw hijiki samples were ground to powder. Total arsenic was measured by ICP-MS with dynamic reaction cell mode after acid digestion of 20 mg powdered sample with 0.5 ml HNO3 and 0.5 ml H2SO4 at 330 °C for 1 hr, dilution to 50 ml, and standard addition calibration; NIES CRM No. 18 urine was used to validate total arsenic, AsBe, and DMA measurements. Speciation extracts used 0.5 g powdered hijiki swollen with 20 ml ultra-pure water, ultrasonic disruption for 1 min, centrifugation at 3000 rpm for 15 min, and adjustment of supernatant to 50 ml. Arsenosugars, AsBe, DMA, and MMA were detected by HPLC-MS/MS with multiple reaction monitoring; arsenic species and water-extracted species totals were measured by HPLC-ICP-MS with PRP-X100 anion-exchange chromatography.
Implications
This source contributes primary occurrence evidence for hijiki seaweed with total arsenic and inorganic arsenic separated in the same samples. The commercial dried-hijiki products had acid-digested total arsenic from 37.1 ± 1.2 to 118.6 ± 11.3 µg As/g dw, while water-extracted inorganic arsenic ranged from 9.2 ± 0.4 to 71.3 ± 2.0 µg As/g dw across all nine samples. The raw and processed hijiki rows should remain on the source’s dry-weight basis, and total arsenic, arsenate/arsenite, DMA, and arsenosugar peaks should not be collapsed into a single arsenic species.
Wiki pages this source may touch
Verification notes
- Identity checks before writing found no existing source page for DOI
10.1248/jhs.56.47, raw handleMFK_shimoda2010, title text, or cite keyshimoda2010-commercial-hijiki-arsenic-speciation. - Text was extracted to
/tmp/hmi-seaweed-058.txtwithpdftotext -layout; Tables 1-4, methods, Results/Discussion, and references were readable. - J-STAGE lists DOI
10.1248/jhs.56.47for this article, although the local PDF text does not print the DOI. - All Key numbers were checked against
/tmp/hmi-seaweed-058.txt, especially Table 1 sample descriptions, Table 3 water-extracted species values, and Table 4 total/water-extracted arsenic summary values. - Units and bases are preserved as
µg As/g dw,%,mgAs/l,µg/l,ml,min, and°C; no unit conversion was performed. - Speciation check: acid-digested total arsenic, water-extracted total arsenic, As(III), As(V), DMA, and individual AsSug peaks are kept distinct. The page treats As(III)+As(V) as the source’s water-extracted iAs and does not substitute total As for iAs.
- Source-side consistency check: the abstract says W-iAs/A-TAs ranged from
24.5to60.1%, while Table 4 reports sample 9 as23.9%; the table value was transcribed as printed and the discrepancy was not corrected. - Brand firewall: consumer brands/stores are not named. Instrument, reagent, and reference-material vendors are retained only as scientific-method context.
- Missing-slug check: no missing product or ingredient slug blockers. Exact hijiki product forms, production systems, and source areas remain in Key numbers while frontmatter uses broad seaweed/kelp food routing.
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.
| Commit | Date | Description |
|---|---|---|
| 4039d20 | 2026-06-10 | scope: broaden ingest to the full upstream+downstream literature (marine, atmospheric, attribution, exposure, toxicology) — inclusion is the default |