Overview
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Key numbers
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- 95%–100% bioavailability in their models. However, recent research suggests that assuming all,
- bioavailability and assimilation is less than 100%. Specifically, 25 studies on fish were reviewed,
- and assimilation efficiencies ranged from 10% to 100% for MeHg and from 2% to 51% for Hg(II).
- MeHg and 0.2% to 94% for Hg(II). The overall absorption estimates ranged from 12% to 79% for MeHg
- and 49% to 69% for Hg(II), and were consistently less than 100%. For both fish and humans, a number
- estimated to reach systemic circulation, and make the assumption that 95% to 100% of the ingested
-
- Fish approximately 80% to 90% of total uptake, with the remaining fraction coming from water (19,20).
- 90%is of total
- variable and may account for 32% to 92% of the total Hg(II) accumulation, with the remainder being may be more important under
- perfused with HgCl2 solution which demonstrated that the majority (78%–85%) of Hg(II) accumulated
- following 30 days dietary exposure to HgCl2 , 36% of the relative Hg(II) burden accumulated in
- MeHgCl for 30 days, less than 3% of the relative Hg(II) burden was found in posterior intestines. Thus,
- We identified 25 studies which report dietary AEs for Hg(II), MeHg, or both (Figure 2; Table S1),
- for MeHg were 10%–100% and for Hg(II) were 2%–51% (Figure 2). In general, dietary MeHg was
- radioisotopes assimilated 56%–95% and 10%–27% of MeHg and Hg(II), respectively (27). Similarly,
- Goto and Wallace (28) reported differences in MeHg AEs (52%–89%) after feeding mummichog
- Fisher (29) reported low dietary AEs for Hg(II) (2%–4%) and MeHg (10%–14%) after feeding killifish
- AEs were significantly greater for both Hg(II) (18%) and MeHg (82%) from this food type, which
- study by Rodgers and Beamish (31), AE decreased from 70% to 80% to less than 50% in rainbow trout
- and reported an AE of 98% regardless of experimental Hg exposure. Conversely, Northern pike
- (Esox lucius) assimilated only 19% of the MeHg from wild-caught common carp (Cyprinus carpio) used
- asTable S2. in Table S2.
- different among the treatment groups, which the authors suggested may have been due 95% of the initial dose to betotransferred
- Beamish (31), AE decreased from 70% to 80% to less than 50% in rainbow trout exposed to dietary MeHgor 16 µg/g wet weight), and
- transfer to other tissues occurred more slowly, as 2 days were required for 95%
- exposure to 203 MeHg and a subsequent 30-day depuration period, 71%–77% of the accumulated
- the head (16%–18%) and viscera (5%–9%) (21). In fish muscle tissue, >95% of the Hg(II) is present as
- absorbed from the intestine than Hg(II) generally holds true, the assumption that MeHg is nearly 100%
- 95%–100% of the ingested MeHg is absorbed into systemic circulation is largely based on limited
- A body of emerging research suggests that Hg may be less than 100% bioavailable from seafood
- absorption) for total Hg, MeHg, or both (Figures 3 and 4; Tables S3 and S5). These studies cover
- Overall mean bioaccessibility estimates ranged from ~2% to 100% for MeHg and 0.2% to 94%
- for total Hg; overall mean absorption estimates ranged from 12% to 79% for MeHg and 49% to 69%
- for total Hg (Figures 3 and 4; Tables S3 and S5). Some of the studies investigated only a single type
- ranged from 21% to 52%, and MeHg bioaccessibility ranged from 20% to 59% from raw seafood in the
- Hong Kong study (52). In vitro total Hg bioaccessibility from 16 raw seafood species in Spain ranged
- of bioavailability) after 2 h of incubation with cultured Caco-2 cells was 49%–69% and 3%–14%,
- from 10 raw seafood species in Montreal ranged from 50% to 100%; absorption after 2 h of incubation
- with cultured Caco-2 cells ranged from 29% to 67% of the initial undigested sample (51). Taken together,
- challenge the assumption that 95%–100% of ingested MeHg is absorbed.
- as outlined in Table S4.
- numbers along the Y-axis indicate studies, as outlined in Table S4.indicate studies, as outlined in Table S4.
Methods (brief)
- the natural environment, or muscle collected from such fish) have rarely (2 of 24 studies) been used as
- Environ. PublicPublic
- natural environment, or muscle collected from such fish) have rarely (2 of 24 studies) been used as a source of rainbow trout (36).
- most likely bound to cysteine residues in proteins (40). This has been substantiated by HPLC-ICP-MS
- their transfer to a different lake. Spiked Hg(II) was detected in muscle samples over the course of
- studies are drawn from small sample sizes. Both studies focus on acute exposures and do not utilize
- in vivo bioaccessibility represents a combined contribution of human and bacterial digestion to
- the apical side). Metabolism of the compound may occur during both digestion/solubilization
- different ways of cooking these seafoods affected Hg bioaccessibility relative to raw samples of the
- the digestion and a longer small intestinal digestion (6 h vs. 2 h). In vitro total Hg bioaccessibility
- with cultured Caco-2 cells ranged from 29% to 67% of the initial undigested sample (51). Taken together,
- seafoods affected Hg bioaccessibility relative to raw samples of the same seafood (53,54).
- bioaccessibility in boiled and fried fish were 40% and 60% lower, respectively, than raw samples of the
- same fish among samples of Spanish mackerel (Scomberomorus maculatus), cat shark (Scyliorhinus sp.)
- methods that use a lower weight of fish to start the digestion and a longer small intestinal digestion (6 h
- and consequently less Hg is solubilized during digestion. The strong affinity of Hg for proteins (67)
- digestion—bioaccessibility
- digestion—bioaccessibility
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)
- Other cooking oils (canola, sunflower, coconut, avocado, sesame)
- Seaweed/kelp foods (nori, wakame, kombu, dulse — as food products)
- Mercury
- Mercury
- Cadmium
- Arsenic
Verification notes
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Update history
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