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:
- reliable and repeatable measures both temporally and spa- methylation potential (Gorski et al. 2008; Wyn et al. 2009;
- a wide range of microbial communities (Fleming et al. hammer et al. 2011; Ackerman et al. 2016; Evers 2018;
- dataset, and therefore using geometric means are preferable or MTI (Pauly and Watson 2005). As a result, a threshold of
- to using arithmetic means. However, the published data trophic level 3.5 was used for visualization for some graphs.
- long-term trends in Hg concentrations in fish and wildlife. and associated aquatic ecosystems (Table 1). Where
- erman et al. 2019; Chételat et al. 2020). Thus, for effec- (range of years covered was 1972 to 2023) emphasized Hg
- Table 1 Potential choices of bioindicator species for ecological and human health as grouped by major terrestrial biomes and their associated aquatic ecosystems (as described and adapted from
- et al. (2008), 96DesGranges et al. (1998), 97Peterson et al. (2016b), 98Reif et al. (2015), 99Krey et al. (2015), 100Perkins et al. (2016), 101Eagles-Smith and Ackerman (2009), 102Eagles-Smith and
- in three risk categories based on mean data derived from a survey of >0.46 = high. Letters indicate additional available fish Hg samples that
- than 75%) are not as high as those in higher trophic level iation. The raw data underlying the averaged statistics used
- fish (>95%; Driscoll et al. 2007). herein were not always available and therefore, individual
- Table 2 Fish Hg concentrations and meal frequency ingestion for people, based on U.S. guidelinesa
- communities (AMAP 2015), and by the World Health ized previously (Depew et al. 2012a, b; Table 3a) and
- (e.g., shellfish such as mussels) at trophic level 2 generally 0.50 µg/g, ww or higher (Depew et al. 2012a) (Table 3a). A
- such as tuna, swordfish and shark can have elevated MeHg risk categories for diet (Table 3a) and various tissue types
- 0.46 µg/g, ww; Table 2)). While the European Union (EU) both laboratory and wildlife populations has improved
- Table 3 a. Screening benchmarks of MeHg in the diet of piscivorous fish and birds for reproductive endpoints. b. Estimated effect Hg concentrations in two broad feeding groups of birds – fish
- Assuming dietary Hg is adjusted for >95% MeHg
- monitoring purposes (Table 4). There are many available maternal transfer of MeHg to offspring during reproduction
- from tissue types for targeted biotic groups (Table 4). influence the interpretation of MeHg concentrations in
- purposes is in the MeHg form (i.e., generally >95%), ana- marine fish (Ward et al. 2010; Baumann et al. 2017). In
- Table 4 Major biota groupings and tissues identified for MeHg monitoring using non-lethal methods
- Fish Muscle fillet 75–95% ww or dw THg or MeHg Bloom (1992); Lescord Recent evidence indicates that
- (but varies on average et al. (2018) %MeHg may be lower for some fish species (Manceau et al. 2021a) and for
- as low as 65%) some cooking approaches (Wang et al. 2013) so to confirm the expected
- amounts. 10% of fish should be analyzed for MeHg content.
- Muscle biopsy 75–95% dw THg Peterson et al. (2004) dw is best because of moisture loss concerns. Muscle biopsy to muscle fillet has
- Blood >95% ww or dw THg Assumed to be >95% MeHg based on other vertebrates.
- Sea turtles Scutes, carapace ~10% fw (or dw if scutes need THg Rodriguez et al. (2019); While scutes are keratinized material the %MeHg may be relatively low and
- Blood >95% ww or dw THg Assumed to be >95% MeHg based on other vertebrates.
- Muscle >95%? ww or dw THg Assumed to be >95% MeHg based on other vertebrates.
- Birds Blood >95% ww or dw THg Rimmer et al. (2005); Elimination of MeHg in adult blood comprises an initial fast phase, with half-
- Dried Blood on >95% dw THg Perkins and Basu Sayers et al. (2023) supports this approach with new caveats.
- Feather ~100% dw or fw whole feathers THg Burger (1993), Renedo Use feathers with care for interpretation; see Peterson et al. (2019) for a tool and
- Rhamphotheca >95% fw THg Outer surface of the beak that consists of a thin sheath of keratin and were 2-fold
- Nails or claws or talons >95% fw THg Hopkins et al. (2007) Total Hg gull ‘claws’ better reflect Hg concentrations in internal organs vs.
- Eggs >96% dw or ww THg Ackerman et al. (2013) Wet weight can be problematic if eggs are not collected immediately after laying
- (96% for 22 species) because of potential moisture loss (Stickel et al. 1973; Dolgova et al. 2018).
- Eggshells and >95% dw THg Peterson et al. (2017) Membranes are assumed to be primarily MeHg, but shells are entirely inorganic
- Muscle >95% ww or dw THg Renedo et al. (2021) MeHg comprised over 99% of total Hg in breast muscle of waterfowl (Sullivan
- Marine Skin >90% dw THg Wagemann et al. (1998) Muktuk (in marine mammals) includes layers of skin and blubber.
- Fur or hair >90% dw (or fw if fur is not THg Evans et al. (2000) Use fur with caution; fur/hair may not relate to blood and muscle depending on
Methods (brief)
- sources of information that should be collected in a stan- Fish trophic levels were assigned by species using
- collected from the published literature include individual reason why, in 2004, the Convention on Biological Diver-
- samples that do not meet strict criteria) or during statistical movement, and physiology in addition to changes in the
- analysis (if sample sizes are sufficient, by including these availability of MeHg in the environment (Chételat et al.
- All biotic samples were assigned a Taxonomic Serial fired power plants and artisanal small-scale gold mining
- Zamani-Ahmadmahmoodi et al. (2009), 215White and Cristol (2014), 216Hill et al. (2008), 217Goutner and Furness (1997), 218Alves et al. (2023), 219Bustamante et al. (2023), 220Quillfeldt et al.
- in three risk categories based on mean data derived from a survey of >0.46 = high. Letters indicate additional available fish Hg samples that
- invertebrates are not considered. Therefore, organisms such The data collected and incorporated into GBMS repre-
- as phyto and zooplankton are not included for biomoni- sent the arithmetic mean, or individual sample concentra-
- the organism sampled (i.e., species, date, location, size/age, major taxonomic group (i.e., cartilaginous and bony fish,
- and tissue analyzed); (2) an appropriate method of sample sea turtles, birds and marine mammals) and tissue type and
- vicianus) and piscivorous waterbirds (common loons, and atomic absorption detection has simplified Hg deter-
- Gavia immer) and is well supported by data collected in mination and made analysis more accessible to those
- can be non-lethally collected in the field. Samples that can transferred from females to their offspring differs among
- Composite samples are sometimes used to estimate popu- animals. For instance, rapid growth of juvenile birds can
- Biota group Tissue type % MeHg Sample preparation Analysis type Source reference Comments about use of tissue type
- Eggs >96% dw or ww THg Ackerman et al. (2013) Wet weight can be problematic if eggs are not collected immediately after laying
- Sample preparation type that is underlined is the preferred type, but the alternative is acceptable if properly performed; Reported as wet weight (ww), dry weight (dw), and/or fresh weight (fw).
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)
- Seaweed/kelp foods (nori, wakame, kombu, dulse — as food products)
- Mercury
- Mercury
- Cadmium
- Arsenic
- Chromium
Verification notes
- Identity check: DOI, raw handle, candidate cite-key, and SHA-256 were compared against existing
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- 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.