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Heavy Metal Index

Health Risk Assessment Attributed to Consumption of Fish

Source

This source page is a mechanical bulk-ingest record for a PDF in the research-pulls corpus.

Page snapshot
Cited by7 pages
Metals measured4
Evidence tierB
Year2022

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:

  • (CVAAS). The total-Hg levels ranged from 0 to 3.159 µg/g. The average concentration in non-
  • Oliveira, M.W.; de Oliveira Lima, M.; carnivorous species (n = 32) was 0.116 µg/g, and among carnivorous fish (n = 43), it was 0.869 µg/g.
  • and 0.1 µg/kg bw/day, respectively. Recent review articles illustrate the magnitude of the
  • of the Negro River. This Basin covers 83% of Roraima, with a drainage area that covers
  • reference material for trace metals (DOLT-4) (% of recovery: 92.24 ± 7.73; 70.92 to 100)
  • and fish protein-certified reference material for trace metals (DORM-3) (% of recovery:
  • is in the form of methylmercury, since, as previously described, more than 90% of the
  • were made: (i) 100% of the mercury detected in the fish samples is in the chemical form of
  • methylmercury (MeHg); and (ii) 100% of the methylmercury present in the fish muscle is
  • an average mercury concentration of 0.31 µg/g (SD 0.29) and median concentration of
  • and median concentration of 0.45 µg/g. Finally, at the Uraricoera River (Collection Point 4),
  • Table 1. Characterization of the fish collected in the Branco River Basin, Roraima, Brazil.
  • The mercury concentration average in non-carnivorous species (n = 32) was 0.116 µg/g
  • (SD 0.126) and the average concentration for carnivorous fish (n = 43) was 0.869 µg/g
  • Table 2 presents the methylmercury doses ingested by different population sub-
  • FAO/WHO 0.45allμg/kg
  • Table 3 presents the risk ratio attributable to the consumption of methylmercury
  • ingested based on fish consumption of 50 g are below the limit of 0.45 µg/kg bw/day, as
  • Table 2. Estimates of mercury doses ingested according to different fish consumption levels and
  • Table 3. Risk ratio attributable to the consumption of fish contaminated by mercury according to the
  • that range from 69 to 96 g per day. Finally, it is not recommended that children aged 2 to
  • Table 4. Calculation of maximum safe fish consumption (in grams per day) according to the U.S.
  • Table 5. Calculation of maximum safe fish consumption (in grams per day) according to
  • of mercury that ranged from 0 to 3.16 µg/g. Of the four collection points selected to
  • the Uraricoera River (57.1%) presented concentrations of methylmercury equal to or above
  • the capital of Boa Vista, the lowest levels of contamination (23.5%) were reported. In this
  • of indigenous people, since mercury levels in blood samples, ranging from - to 62.6 µg/L
  • Sing et al. (49) found lower levels of contamination (ranging from 2.0 to 31.3 µg/L in
  • 40% of the participants presented hair mercury concentrations above 6.0 µg/g. Finally,
  • et al. (43) identified median concentrations of mercury in the hair of Yanomami who live
  • had almost a 3 times greater risk (RC: 2.91; CI95% 1.26–7.28) of developing high levels
  • hair mercury levels above 2.0 µg/g represented a 69% higher risk of suffering an acute
  • fish, we assume that 100% of the mercury present in the muscle of the fish collected
  • is in the form of methylmercury, and 100% of this mercury is absorbed by the human
  • The Netherlands, 2016. Available online: http://www.fao.org/fao-who-codexalimentarius/sh-proxy/en/?lnk=1&url=https%25
  • 3A%252F%252Fworkspace.fao.org%252Fsites%252Fcodex%252FMeetings%252FCX-735-10%252FReport%252FREP16_CFe.pdf

Methods (brief)

  • four trophic levels (i.e., herbivore, omnivore, detritivore, and carnivore), were collected at four
  • locations in the Branco River Basin. The fish samples were sent to the Toxicology Laboratory at
  • Evandro Chagas Institute to determine the total-Hg levels by using the cold vapor atomic system
  • (CVAAS). The total-Hg levels ranged from 0 to 3.159 µg/g. The average concentration in non-
  • Basta, P.C. Health Risk Assessment The weighted average of contamination levels for all samples was 0.545 µg/g. The health risk
  • the locations sampled is at high risk attributable to mercury ingestion, with the only exception of
  • problem by revealing the methylmercury levels detected in hair samples of individuals
  • levels in freshwater fish collected in the Rio Branco Basin and commercialized in the markets
  • Collection and Storage of Fish Samples
  • Fish were collected from the following four locations in the Branco River Basin (Figure 1):
  • ice and shipped to Boa Vista. Each sample was photographed, and the information on
  • The taxonomic identification of each specimen collected was confirmed to the maxi-
  • cooler with ice and shipped to Boa Vista. Each sample was photographed, and the
  • g. The samples common
  • The taxonomic identification of each specimen collected was confirmed to the
  • dorsal part of each specimen, which was divided into 3 portions of roughly 2 g. The samples
  • The total mercury (THg) determination in fish samples was carried out at the Tox-
  • proposed by Akagi et al. (55). For each sample, 0.3 to 0.5 g of muscle tissue was weighed

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.

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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.

CommitDateChangeDescription
b01ec52c2026-08-04major2 sections added
d49e450f2026-08-03major5 sections added; narrative text revised