Overview
Kennedy and colleagues modeled methylmercury exposure from Mediterranean seafood by combining a large seafood contamination literature dataset with seafood supply/provenance data from ARTIS and consumption estimates from the Global Dietary Database. The paper is a transdisciplinary exposure and cost-of-illness analysis, not a new laboratory survey.
The contamination dataset uses total Hg and MeHg observations from the literature. For risk assessment, total Hg concentrations were converted to MeHg using EFSA conversion factors: 1.0 for fish and 0.8 for molluscs/crustaceans.
Key numbers
Literature-screening and dataset construction:
| Field | Value |
|---|---|
| Initial manually screened papers | 73 |
| Initial observations | 25,152 |
| Cinnirella et al. 2019 observations in initial dataset | 24,465 |
| Final (Me)Hg database | 17,964 data points |
| Final edible-tissue observations after FAO-division refinement | 17,934 |
| Mediterranean marine species represented | 267 |
| FAO divisions included | 7 |
| Sampling period covered by final dataset | 1969-2019 |
| Observations from Cinnirella et al. 2019 in final refined dataset | 17,296 |
Share of seafood-category observations above JECFA concentration limits:
| Seafood group | Above 0.5 ug/g wet weight | Above 1.0 ug/g wet weight | Above 2.5 ug/g wet weight |
|---|---|---|---|
| Small pelagic marine fish | 1.6% | - | - |
| Molluscs | 7.62% | - | - |
| Small demersal marine fish | 20.8% | - | - |
| Large demersal marine fish | 23.7% | 11.4% | 2.39% |
| Cephalopods | 29.4% | - | - |
| Crustaceans | 39.8% | 12.3% | - |
| Large pelagic marine fish | 49.3% | 26.2% | 4.27% |
Table 1 reports mean MeHg levels in ug/g wet weight by seafood group and Mediterranean FAO division. The prefixes S_ and L_ denote small (trophic level < 4) and large (trophic level >= 4) demersal fish and pelagic fish.
| FAO group | Balearic 37.1.1 mean (n) | Gulf of Lions 37.1.2 mean (n) | Sardinia 37.1.3 mean (n) | Adriatic 37.2.1 mean (n) | Ionian 37.2.2 mean (n) | Aegean 37.3.1 mean (n) | Levant 37.3.2 mean (n) |
|---|---|---|---|---|---|---|---|
| Cephalopods | 0.19 (16) | 0.33 (*) | 0.47 (283) | 0.16 (3) | 0.05 (53) | 0.09 (**) | 0.14 (8) |
| Molluscs excl. cephalopods | 0.05 (866) | 0.02 (1830) | 0.46 (2205) | 0.11 (1672) | 0.22 (496) | 0.07 (247) | 0.16 (965) |
| Crustaceans | 0.26 (423) | 1.06 (5) | 0.72 (849) | 0.19 (24) | 0.30 (44) | 0.24 (54) | 0.05 (42) |
| S_DF | 0.17 (1025) | 0.21 (193) | 0.87 (1394) | 0.51 (234) | 0.40 (330) | 0.16 (329) | 0.24 (1618) |
| S_PF | 0.13 (329) | 0.06 (12) | 0.19 (481) | 0.15 (105) | 0.17 (77) | 0.24 (9) | 0.13 (89) |
| L_DF | 1.15 (35) | 0.59 (115) | 0.59 (184) | 0.24 (46) | 1.09 (56) | 0.12 (32) | 0.20 (242) |
| L_PF | 1.09 (177) | 1.11 (206) | 1.60 (272) | 0.66 (30) | 0.50 (146) | 0.28 (23) | 0.11 (59) |
| Total n | 2871 | 2361 | 5668 | 2114 | 1202 | 694 | 3023 |
Table 1 footnotes state that Gulf of Lions cephalopod MeHg was estimated from the arithmetic mean of neighboring FAO Divisions 37.1.1 and 37.1.3, and that Aegean cephalopod MeHg was estimated from the arithmetic mean of neighboring divisions. The Aegean footnote prints 37.2.2 and 37.3.1; this page preserves the source wording.
Other source-reported values:
| Finding | Value |
|---|---|
| Mediterranean mussel (Mytilus galloprovincialis) MeHg range | 0.001-23.6 ug/g wet weight |
| Mediterranean seafood harvested in the region but exported outside it | 16.46% |
| Countries estimated to exceed JECFA PTWI only under high-contamination 75th/90th percentile scenarios | Tunisia, Libya, Algeria |
| JECFA PTWI used in the paper | 1.6 ug/kg body weight/week |
| EFSA TWI cited in introduction | 1.3 ug/kg body weight/week |
| EU general fishery-products limit cited in introduction | 0.5 mg/kg fresh weight |
| EU species-specific exceptions cited in introduction | 0.3 or 1.0 mg/kg fresh weight |
| ATSDR chronic MRL cited in introduction | 0.1 ug/kg body weight/day |
| Hair-Hg reference level associated with ATSDR chronic MRL | about 1 ug/g hair |
| Lower hair-Hg cut-off described from updated calculations | 0.58 ug/g hair |
| Dose-response used for IQ calculation | 0.18 IQ-point decrease per 1 ug/g increase in maternal hair mercury |
| IQ distribution assumption | Mean 100, SD 15 |
| U.S. lifetime productivity at birth used as base estimate | $1,468,669 in 2016 |
| U.S. market productivity component | $934,583 |
| U.S. non-market productivity component | $534,086 |
| GDP deflator used to convert to 2021 prices | 1.122 |
| Productivity value per IQ point after adjustment | $23,070 in constant 2021 USD |
| Estimated annual Mediterranean economic loss from MeHg-linked IQ decline | More than 10 billion EUR |
| Countries with total modeled costs exceeding 1 billion EUR under both adjustment types | Egypt, France, Turkey, Italy, Algeria, Morocco |
| Countries exceeding 2.2 billion EUR in the alternative cost adjustment discussed | Turkey, France, Egypt |
Methods (brief)
The authors searched Scopus and PubMed for "mediterranean" AND "mercury" in titles and abstracts, limited to publications from 2015-2022, then manually screened papers for relevant seafood MeHg/Hg estimates. They combined newly screened observations with Cinnirella et al. 2019’s Mediterranean biota Hg compilation.
The dataset was refined to FAO Mediterranean divisions 37.1, 37.2, and 37.3, excluding unclear fishing areas, Black Sea and Marmara Sea observations, inedible or rarely consumed species, non-edible tissues, and duplicate total-Hg observations where MeHg was reported for the same study/species/tissue/location combination. Observations were harmonized to ug/g; wet/dry-weight conversions followed Cinnirella et al. 2019 where needed, and unspecified weight type was assumed to be wet weight.
Seafood consumption and provenance modeling combined ARTIS supply data, FAO capture statistics, GDD consumption estimates, IHME population data, edible-weight conversion factors, and rfishbase trophic-level assignments. Economic cost estimates linked modeled prenatal MeHg exposure to IQ loss and productivity loss.
Implications
This source is useful as B-tier synthesized seafood evidence for Mediterranean MeHg exposure, especially for differentiating large predatory marine fish from smaller fish and shellfish. It also documents that international trade can shift seafood contamination exposure between regions.
Because the paper is a modeling and literature-synthesis study, its values should not be treated as a new primary occurrence survey. The compiled Table 1 means are useful for route-level context and gap targeting; species-level benchmark pooling should use the underlying primary records or the authors’ data/codebook where available.
Wiki pages this source may touch
- Fish — marine, predatory (tuna, swordfish, shark, king mackerel)
- Fish — marine, non-predatory (sardines, anchovies, salmon, cod)
- Shellfish (shrimp, crab, lobster, clams, oysters, mussels)
- Mercury
- Methylmercury
Verification notes
- Identity check: DOI
10.1016/j.scitotenv.2024.177953, raw handleRPMEHG_10-1016-j-scitotenv-2024-177953, candidate cite-keykennedy2025-mediterranean-seafood-methylmercury, and SHA-256d00864dad0663ba0b1ff794fded990a6a99a0e69778827d4e1029b9342366626were searched before creation; no existing clean post-2026-05-14 source page was found. - Full-PDF read performed from the 13-page Science of the Total Environment PDF. Table 1 and all main-text numeric findings captured above were checked from
pdftotext -layout; figures were read for qualitative country-pattern findings only, without digitizing plotted bars. Supplementary tables and R code are referenced by the paper but were not bundled in the local PDF. - Brand firewall: the source reports seafood groups, species, countries, and FAO fishing divisions, not branded commercial products.
- HMTc firewall: page records source facts only; no certification threshold, percentile, or pass/fail calculation is derived from this source.
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. When DOI minting comes online (see schema docs), each entry below will also link to a version-pinned DataCite DOI.