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:
- sampling in Lake Jugla (minimum length 75 cm) and is used consistently in tables and fig-
- posites (n = 119 pooled composites). A predefined core nutrient panel was available for
- coverage in the core nutrient panel were: fat (100.0%), protein (100.0%), metals (100.0%),
- iodine (93.7%), fatty acids (91.0%), and PFASs (83.6%) (see Table S1, Supplementary Materials;
- methylmercury (MeHg) was estimated conservatively as 95% of the total mercury content
- extracted with 25% TMAH at 85 ◦ C for 3 h. Tellurium (Te) was used as an internal standard
- ally evaluated LB (0), MB (LOQ/2), and UB (LOQ) substitution and summarized its effect
- Table S6). Where Σ4 PFAS (Σ4 PFAS = PFOS + PFOA + PFNA + PFHxS; sum on wet weight
- (e.g., Hg/MeHg in mg/kg ww; Σ4 PFAS in µg/kg ww) and Cons is weekly fish consump-
- µg/kg bw/week; Σ4 PFAS TWI in ng/kg bw/week). Accordingly, the weekly intake per
- the EFSA TWI for MeHg (1.3 µg/kg bw/week) (5). For PFASs, exposure was characterized
- A nutritional index (0–1 scale) was calculated as the arithmetic mean of the capped
- Left-censored sensitivity (iodine and Σ4 PFAS). Left-censored results (<LOQ) were
- addressed in the main analysis using middle-bound substitution (MB = LOQ/2). To quan-
- lower-bound (LB = 0) and upper-bound (UB = LOQ) substitution for iodine and Σ4 PFAS.
- and limiting hazard). Results are summarized in Supplementary Table S6.
- pends on the nutritional index specification and LC handling (Supplementary Tables S6 and S7).
- MeHg risk ratio at 300 g/week ranged from 0.08 (well below the TWI) up to 3.48 in the
- PFAS data were available) ranged from 0.06 to 0.66, meaning that none of the measured
- single stratum (Usma–Roach) (Supplementary Table S6). At the lake level, total mercury
- 15–25% of the ~406 g/week protein reference for 300 g of fish consumption (reflecting the
- with iodine contributing minimally across strata (Figure 4; Supplementary Table S6).
- Supplementary Table S3 and visualized in Figure 5. In total, 20/30 strata were categorized
- can be compared to European Union maximum levels for mercury in fish (0.5 mg/kg wet
- for the sum of PFOS, PFOA, PFNA, and PFHxS. In our dataset, Σ4 PFAS median concen-
- trations were far below these limits (the highest median Σ4 PFAS was <1 µg/kg), which
- at 100% of daily needs. This was a conservative choice taken to avoid, for example, oily fish
- (Supplementary Table S6). Seasonality is another representativeness constraint. Samples
- (Supplementary Table S3). If those groups in fact had undetected PFASs, their true safe
- Latvian dataset, PFOA showed low detection frequency and concentrations (45% detection;
- mean 0.01 ng/g ww), whereas PFOS dominated the PFAS profile (~60% of total selected
- range of foods (including freshwater fish) to support dietary exposure assessments (7). In
- construction (Supplementary Tables S6 and S7). EFSA’s risk–benefit assessment guidance
Methods (brief)
- pooled samples stratified by lakes and species. Risks were characterized for methylmercury,
- ments were left-censored and constant after limit of quantification (LOQ) handling. This
- assessment (RBA) for Latvian inland lake fish using pooled samples stratified by lake and
- Fish samples were collected from five major inland lakes in Latvia: Burtnieks, Jugla,
- threshold provides a policy-relevant ‘high-end’ stratum rather than a representative sample
- collected across the five lakes, comprising 72 perch, 73 pike, 84 tench, 79 bream, 91 roach,
- posite samples based on species and lake of origin. The pooled composites were prepared
- number of available pooled composites differs by analyte. Each composite sample consisted
- posites typically consisted of 5–7 individual fish samples. Where individual sub-samples
- composites), noting that sub-sample documentation is incomplete for many composites.
- Samples were collected during two distinct periods: Autumn (September–October
-
- and Summer (July–August 2025). While 134 pooled composites were collected in
- pooled sample counts by lake × species are summarized in Table S2).
- plasma mass spectrometry (ICP-MS) following high-pressure digestion, according to LVS
- EN 15763:2010 (15). Samples were digested with nitric acid (HNO3 ) and hydrogen peroxide
- (H2 O2 ) in a microwave system. Gold (Au) was added to the standard and sample solu-
- (LOQ) was sufficient to detect relevant environmental levels, and measurement accuracy
- these analytes were below the method LOQs and therefore did not contribute meaningfully
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
- Canned seafood (with tin flag)
- Fish — marine, predatory (tuna, swordfish, shark, king mackerel)
- 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.