Fattorini 2006 - Marine-organism arsenic speciation
Fattorini, Notti, and Regoli measured total arsenic and selected arsenic species in bivalves, crustaceans, and fish from temperate, tropical, and polar marine environments. The paper is a baseline bioaccumulation study rather than a market-basket survey, but it reports edible soft parts for crustaceans, whole soft tissues for bivalves, and fish muscle fillets. Total arsenic and inorganic arsenic are separate signals; most speciation rows are dominated by organic arsenic compounds.
Key numbers
The abstract summarizes the overall total-arsenic range as less than 5 to about 200 µg g−1, with Mediterranean crustaceans about 45-110 µg g−1 and tropical crustaceans lower than 30 µg g−1. Concentrations are reported as µg g−1 dry weight.
Selected bivalve total-arsenic results from Figure 1 and the Results text:
| Bivalve species | Location | n | Total As (µg g−1 dry weight) |
|---|---|---|---|
| Adamussium colbecki | Terra Nova Bay, Ross Sea | 15 | 10.9 +- 1.02 |
| Crassostrea virginica | Cienfuegos Bay, Caribbean Sea | 15 | 10.6 +- 1.18 |
| Isognomon alatus | Cienfuegos Bay, Caribbean Sea | 15 | 13.2 +- 1.17 |
| Mytilus galloprovincialis | Adriatic Sea, Mediterranean | 60 | 14.7 +- 4.10 |
| Yoldia eightsii | Terra Nova Bay, Ross Sea | 15 | 186 +- 11.5 |
Selected crustacean total-arsenic results from Figure 2 and the Results text:
| Crustacean species | Location | n | Total As (µg g−1 dry weight) |
|---|---|---|---|
| Litopenaeus schmittii | Cienfuegos Bay, Caribbean Sea | 6 | 10.5 +- 2.86 |
| Farfantepenaeus notialis | Cienfuegos Bay, Caribbean Sea | 8 | 16.3 +- 5.39 |
| Callinectes sapidus | Cienfuegos Bay, Caribbean Sea | 5 | 28.2 +- 6.84 |
| Melicertus kerathurus | Adriatic Sea, Mediterranean | 5 | 46.5 +- 11.1 |
| Nephrops norvegicus | Adriatic Sea, Mediterranean | 5 | 57.3 +- 13.2 |
| Squilla mantis | Adriatic Sea, Mediterranean | 5 | 79.5 +- 28.9 |
| Carcinus mediterraneus | Adriatic Sea, Mediterranean | 5 | 112 +- 46.8 |
For fish muscle, the Results text gives ranges and extremes rather than a full table in extractable text. Caribbean fish muscle ranged from Caranx hippos 2.18 +- 0.55 µg g−1 to Haemulon sp. 26.5 +- 0.77 µg g−1. Mediterranean fish muscle ranged from Sphyraena sphyraena 5.19 +- 2.47 µg g−1 to Scyliorhinus canicula 34.9 +- 6.84 µg g−1.
Table 2 reports arsenic-speciation percentages in selected species:
| Species row | Matrix | iAs (%) | DMA (%) | TMAO (%) | TETRA (%) | AsB (%) | AsC (%) | Unknown (%) |
|---|---|---|---|---|---|---|---|---|
| Mytilus galloprovincialis | Mussel | not reported | not reported | not reported | 12.7 | 67.4 | 19.9 | not reported |
| Callinectes sapidus | Crab | 1.2 | not reported | not reported | not reported | 95.2 | 1.7 | 1.9 |
| Farfantepenaeus notialis | Shrimp | not reported | not reported | not reported | not reported | 7.1 | 92.9 | not reported |
| Haemulon sp. | Fish | 0.5 | not reported | 0.6 | 1.8 | 0.4 | 96.7 | not reported |
| Lutjanus synagris | Fish | 3.77 | 2.06 | not reported | 2.97 | 2.06 | 89.14 | not reported |
Methods (brief)
Samples were taken from Mediterranean coastal and trawling areas in the Adriatic, Ionian, and Tyrrhenian Seas; Cienfuegos Bay, Cuba; and Terra Nova Bay in the Antarctic Ross Sea. Bivalve samples used whole soft tissues of at least three specimens, crustacean samples used edible soft parts after removing carapaces, legs, and chelipeds, and fish were dissected into muscle fillets with liver also analyzed for some species. Samples were dried overnight at 60 °C, microwave-digested with hydrogen peroxide and nitric acid, and analyzed for total arsenic by graphite-furnace AAS with Zeeman correction. Speciation used methanol extraction, HPLC separation, and arsenic measurement in collected fractions.
Implications
This source provides baseline dry-weight arsenic occurrence context for fish, shellfish, and bivalve molluscs across tropical and Mediterranean seafood taxa. It supports broad seafood routing but should not be treated as a retail or jurisdiction-specific market benchmark. The speciation table indicates that inorganic arsenic was low in the representative unpolluted seafood rows, while total arsenic varied substantially by species and taxon.
Verification notes
- PDF text was extracted with
pdftotext -layout; title page, Table 1, Results sections 3.1-3.4, and Table 2 were checked in/tmp/f3_texts/fattorini2006.txt. - DOI
10.1080/02757540600917328, raw handleMFK_fattorini2006, and cite-key checks found no existing source page before creation. - Values were copied from source text and table output as dry-weight
µg g−1values; no conversion to wet weight or mg/kg was performed. - Speciation: Table 2 reports inorganic arsenic percentages only for crab, Haemulon sp., and Lutjanus synagris rows. Total arsenic in all other rows remains
tAscontext and is not promoted to iAs. - Brand firewall: no branded products are reported.
- Frontmatter slugs were checked against
docs/gpt-collaboration/taxonomy-snapshot.md; species-specific seafood product rows are not in the closed vocabulary, so broad seafood/fish/shellfish routing is used.
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 |
|---|---|---|
| 1476f44 | 2026-06-09 | ingest: cacic2019-hemp-heavy-metals fresh from MFK/June 9 |