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:
- regulation). In the survey, 64% of the respondents indicated that hardly represent exemplary RAs and illustrate how HBM can be used in RA and
- (children and aligned studies neuropathy mg/kg bw/d) for neoplastic effects converted into external was used to estimate cancer Mahiout et al., 2022b)
- BMDL10 value (0.43 mg/kg bw/d) levels, with the provisional
- Workers data), urinary o- Commission et al., 2017b) based with a FUE of 0.75 and PBPK risks. Mean and P95 levels of
- (adults) toluidine including on BMDL10 (42.2 mg/kg bw/d) modelling was used to convert the urinary o-toluidine levels,
- Arsenic: inorganic General Published data from Lung, bladder, and skin BMDL 0.5 = 3.0 μg/kg bw/ The sum of iAS, MMA and Cancer risk was estimated on Mahiout et al. (2022b)
- Table 1 (continued )
- literature and vascular complications value of 6.4 μg/L for P95 levels with BE value.
- Bisphenols: bisphenol A General Published data from BPA: effect on renal mean Urinary total HBM-GVGenPop of nr P95 reported in the aligned (Mahiout et al., 2022b;
- (BPA), bisphenol S (adults) literature and relative weight in animals ( 230 μg/L and 1.0 μg/L were used studies were compared to the Meslin et al., 2022)
- Table 1 (continued )
- (4,4′ -methylene (adults) for metabolites MDA, (BHR) 0.12–0.19 μg/m3 NCO causes 2% 2,4/2,6-TDI were basis of the estimated (2023)
- Flame retardants: tris General HBM4EU-aligned Kidney toxicity Several health-based guidance HBM data was used to Arithmetic mean and P95 Plichta et al. (2022)
- 5 phosphate (TDCIPP) 0.007mg/kg bw/d for TCEP ( from a Belgium food basket
- US-EPA, 2009), RfD of 80 μg/kg study (Poma et al., 2018) and
- bw/d for TCIPP, 22 μg/kg bw/d dietary intake was estimated
- for TCEP and 15 μg/kg bw/d for on the basis of national food
- children, data on blood lead neurotoxicity (lost cognitive − 0.054 (95% CI: -0.034 to years (DALYs, per 100,000)
- adults) 100 μg/L; − 0.019 (95% CI: -0.012 Children/adolescents: DALYs
- 200 and 300 μg/L (Lanphear et al., points (FSIQ) loss attributable
- 2005; Remy et al., 2019) to BLL above 20 μg/L.
- chapters I –XVIII and XXc; cause mortality; 1.37 (95%CI: and corresponding hazard
- Table 1 (continued )
- and 95% confidence interval.
- Mercury: General Public literature data Neurotoxicity HQd approach: HBM-GV 5 μg/L EFSA TWI/TDI was converted HQ approach: HQ were (Dominguez-Morueco
- EFSA approach: TWI of 1.3 μg/kg Esteban-Lopez et al., 2022; EFSA approach: Exposure
- equivalent to a TDI of 0.19 μg/kg 1990) P95) compared to tolerable
- Mycotoxins: General Public literature data Reduced body weight gain in HBGV: TDI 1 μg/kg bw/day Probable daily intakes were Two approaches: (Alvito et al., 2022;
- deoxynivalenol and its (children, and HBM4EU-aligned experimental animals HBM-GV 23 μg/L for urinary total reverse-calculated from DON I) hazard quotient calculated Mahiout et al., 2022b)
- DON approach (Apel et al., 2020) median, maximum) to TDI
- Table 1 (continued )
- cyfluthrin, (adults and data), based on urinary neurotoxicity. exposure: derivation of screening using the urinary mass- (median and P95 and their
- Table 1 (continued )
- 0.19 mg/L for MnBP, 0.23 mg/L summed to obtain individual
- and 5-OH-MEHP; 0.12 mg/L for for other anti-androgenic
- MnBP, 0.16 mg/L for MiBP; 2 mg/ substances not assessed.
- mg/kg bw/day from the most forward calculation was 0.01.
- Table 1. The detailed, full RAs or EBoD calculations have been published
- can be used in chemical RA or EBoD calculations, and to demonstrate the in the references provided in Table 1.
- burden of disease related to environmental chemical risk factors. EBoD 2022b). The measured geometric mean (GM) and P95 levels of AAMA
- calculations were made following the principles described in (Hänninen (20–100 μg/L and 70–510 μg/l, respectively) in adults and children were
- internal exposure (examples provided in Supplementary Table 2), ripheral neuropathy risk of acrylamide, provisional HBM-GV was
Methods (brief)
- arsenic (iAs), (infants, literature and cancer d defined by (WHO/FAO, 2011) DMA levels was converted the basis of the urinary
- acid (MMA) and adolescents, studies (aggregated extrapolation as explained by urinary mass-balance DMA, converted into external
- (DMA) 2017a). This resulted in a cancer with an FUE used earlier by ( calculated using the cancer
- studies (aggregated (As(III)+As(V)+MMA + DMA) (
- included. The HBM4EU-aligned studies were surveys that collected HBM The main uncertainty in this RA was related to the limited HBM data on
- samples and data in as harmonised a way as possible from (national) both the general population in Europe and workers, as o-toluidine was
- 2021). In addition, DMF samples from the ESB were analysed for the comparison with the revised tolerable daily intake (TDI), recently
- MMA and DMA (Mahiout et al., 2022b). The HBM data from the liter conducted in three European countries (Belgium, France and Spain)
- DMA in food. Analytical challenges related to the speciation of As spe welding and chromium-plating activities (Mahiout et al., 2022a) were
- approximately 1000 HBM samples from 2008 to 2021, sent to FIOH for (FUE), was limited. For TCIPP and TCEP, FUE was derived from TDCIPP
- exposure monitoring by occupational health service units. Urinary data. In addition, the limit of detection (LOD) and limit of quantification
- diamine levels were converted into external isocyanate (NCO) air levels (LOQ) values for the analytical methods were quite high in both bio
- on studies collected at different time periods (2004–2020) and the percentiles of exposure, and thus did not represent a potential health
- association between developmental neurotoxicity and BLL, the dos DON was associated with the fact that the first morning void samples
- et al., 2022b). U-TCPy was at detectable levels in most samples, with the
- Cyprus, France, Israel, the Netherlands, and Israel. Adults were sampled studies, such as sampling period, sampling collection method, sampling
- the RA may still be common to more than one substance, making it available HBM studies, i.e., different sampling periods, sample collec
- (sampling period 2014–2018) (Mahiout et al., 2022b). Urinary levels of sentativeness of the sampled population.
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)
- Baby Sunscreen, Mineral (ZnO + TiO2)
- Mercury
- Mercury
- Cadmium
- Lead
- Arsenic
- Nickel
- Tin
- Chromium
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.