Overview
This source page is a mechanical bulk-ingest record for a PDF in the research-pulls corpus. It preserves source-level identity, routeable product/analyte scope, and exact extracted numeric lines for later human or fresh-context audit. It does not derive HMTc thresholds, percentiles, or brand-by-brand comparisons.
Key numbers
The worker extracted the full PDF text with layout preservation twice and compared extraction hashes before commit. The following lines are copied from numeric/table-bearing regions of the PDF and retain the source units and wording where legible:
- the tolerable weekly intake (TWI) of 4 μg/kg body weight (bw), expressed as mer-
- than the TWI (1.3 μg/kg bw per week, expressed as mercury) established by EFSA
- The CONTAM Panel established a tolerable weekly intake (TWI) for inorganic mercury of 4 μg/kg bw, based on a BMDL10
- of 0.06 mg/kg bw per day (expressed as Hg), for increase in kidney weight in male rats (NTP, 19932), applying an UF of 100
- and converted to a weekly basis expressed as mercury. For methylmercury, a TWI of 1.3 μg/kg bw, expressed as mercury,
- was established based on a NOEL for neurodevelopmental effects from the Seychelles nutrition cohort of 11 mg/kg mater-
- nal hair (Lynch et al., 20113) and on a BMDL05 for neurodevelopmental effects from the Faroese cohort 1 of 12 mg/kg in
- maternal hair (FAO/WHO, 20044), resulting in 11.5 mg/kg maternal hair concentration causing no appreciable adverse ef-
- This was converted to a maternal blood mercury concentration of 46 μg/L and, using a toxicokinetic model, further con-
- verted to a dietary mercury intake of 1.2 μg/kg bw. An UF of 2 for variation in the hair to blood ratio and a standard factor
- in consequence a daily dose of 0.19 μg/kg bw that was converted to a weekly basis.
- In the EFSA (2012) assessment, mean dietary exposures across age groups did not exceed the TWI for methylmercury
- food (EFSA CONTAM Panel, 2012), a tolerable weekly intake (TWI) for inorganic mercury of 4 μg/kg body weight (bw), ex-
- For methylmercury, a TWI of 1.3 μg/kg bw, expressed as mercury, was established based on neurodevelopmental effects
- In 2012, the EFSA CONTAM Panel established a TWI for inorganic mercury of 4 μg/kg bw, expressed as mercury, thus follow-
- kidneys. Doses of 0.312, 0.625, 1.25, 2.5 or 5 mg/kg bw/day were tested in the 6-month study administered 5 days/week
- and 0.625 (females) mg/kg mercuric chloride, respectively, accompanied by minimal to mild nephropathological find-
- male rats in this study as the pivotal effect for deriving a HBGV. Based on the BMDL10 of 0.06 mg/kg bw/day, expressed
- weekly basis and rounding to one significant figure, the Panel established a TWI for inorganic mercury of 4 μg/kg bw,
- in adult albino Wistar rats. Six animals per group either received distilled water as control or 0.02 mg/kg bw/day mercury
- stantiate their findings. Therefore, EFSA does not consider the study by Apaydın et al. (2016) suitable to derive a reference
- mercury is not needed based on the results presented by ATSDR from 2024. The TWI for inorganic mercury of 4 μg/kg bw,
- 11 mg/kg, ‘the beneficial effects associated with maternal n-3 long-chain polyunsaturated fatty acids (n-3 LCPUFAs)29 no longer
- imately 11 mg/kg as an ‘apparent NOEL’. However, it was noted that the number of observations at higher exposure levels
- BMDL05 of 12 mg/kg methylmercury in maternal hair that had previously been established from this study by JECFA (FAO/
- BMDL05 value of 12 mg/kg methylmercury in maternal hair.
- EFSA then used the maternal hair mercury concentrations from the Seychelles and Faroese studies (mean of 11.5 mg/
- netic model yielded a corresponding steady-state intake of 1.2 μg/kg bw/day. A composite uncertainty factor of 6.4 was
- intake (TWI) of 1.3 μg/kg bw, expressed as mercury.
- corresponds to a maternal hair concentration of 5.56 mg/kg. This value was converted to an intake of 0.41 μg/kg/day using
- the TWI (of 1.3 μg/kg bw, expressed as mercury) established by EFSA in 2012.
- approximately 5 points). These small decrements may represent meaningful intellectual and economic achievement at a popu-
- et al., 1997; US EPA, 2001). Using a benchmark response (BMR) of 5%, the resulting BMDL05 values ranged approximately
- from 10 to 15 mg/kg methylmercury in maternal hair. EFSA adopted the value of 12 mg/kg methylmercury in maternal hair
- For the Seychelles cohort, EFSA identified an ‘apparent NOEL’ of 11 mg/kg methylmercury in maternal hair based on the
- estimated slopes ranging from 140 to 370 and a mean of approximately 250, and notes that the World Health Organization
- factor of 3 for human variability’, but no UF was applied for hair to blood conversion (see Table A2 in Appendix 1).
- 11.5 mg/kg methylmercury in maternal hair, recruited approximately 300 pregnant women in 2001 and followed offspring
- Zealand), a reference point of 5.56 mg/kg methylmercury in maternal hair was derived.
- • EFSA, in contrast, derived a reference point of 11.5 mg/kg methylmercury in maternal hair based on cohorts from the
- values that differ by approximately a factor of two on a weekly basis (0.7 vs. 1.3 μg/kg bw/week).
- the current EFSA TWI of 1.3 μg/kg bw per week, expressed as mercury, remains valid.
Methods (brief)
- minated diphenyl ethers (PBDEs), inorganic arsenic, dimethylarsinic acid (DMA), inorganic mercury and methylmercury.
- acid (DMA), inorganic mercury and methylmercury13 in fish. For these contaminants, except mercury, the assessments were
- tested, small sample size (6 instead of 10 animals tested per dose as suggested in respective guidelines) and no information
- kidney is given, and it is not reported whether or not sample blinding was implemented prior to evaluation, which would
- DMA dimethylarsinic acid
- Hack, M., Taylor, H. G., Drotar, D., Schluchter, M., Cartar, L., Wilson-Costello, D., Klein, N., Friedman, H., Mercuri-Minich, N., & Morrow, M. (2005). Poor pre-
Implications
This page makes the source discoverable for category-level evidence routing. Values remain source-native and should be used only with the stated matrix, species, basis, geography, and censoring context from the paper. The page does not convert total mercury to methylmercury or use total arsenic as inorganic arsenic.
Wiki pages this source may touch
- Fish — marine, non-predatory (sardines, anchovies, salmon, cod)
- Shellfish (shrimp, crab, lobster, clams, oysters, mussels)
- Mercury
- Mercury
- Cadmium
- Lead
- Arsenic
Verification notes
- Identity check: DOI, raw handle, candidate cite-key, and SHA-256 were compared against existing
wiki/sources/pages before creation. - Full-PDF read:
pdftotext -layoutwas run on the full PDF twice; extracted text hashes matched before the page was written. - Numeric verification: numeric/table-bearing lines were selected mechanically from the verified extraction and preserved without unit conversion or rounding.
- Brand firewall: the worker skips PDFs when extracted numeric lines appear brand/manufacturer-sensitive; this page contains category-level or species-level evidence only.
- HMTc firewall: no threshold, percentile, pass/fail, clean/dirty, or certification math is stated.
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.