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Heavy Metal Index

Hair mercury levels in Amazonian populations: spatial distribution

Source

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

Page snapshot
Cited by5 pages
Metals measured3
Evidence tierB
Year2009

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:

  • mercury means range from 1.1 to 34.2 μg/g. Most studies did not show any significant difference in
  • as cardiovascular deleterious effects (5,34-37). It was not and the absence of a measure of central tendency (mean,
  • intake lower than 1.5 μg/kg of body weight (41). The Envi- We presented the results from all the selected articles in
  • Dose (RfD) at 0.1 μg/kg/day, expecting no more than 11 cury levels and fish consumption measures when availa-
  • μg/g of mercury in maternal hair (42). Most researchers ble. The tables were organized by regions and using the
  • μg/g of hair mercury (36,43). from Andean Amazonian countries (Table 1) and French
  • late eighties, showing quite complete information about or group (Tables 6, 7, 8, 9). Finally, the studies from the
  • Table 1: Hair mercury levels in Andean Amazonian Countries
  • Studied population Study N Hg mean μg/g Range > 10 μg/ga Fish
  • Barbieri et al. 2009 Cachuela Esperanza 150 3.76 (3.01) (2.52) 0.42-15.65 3% 10.5 meals/week
  • Monrroy et al. 2008 Upper Beni River 556 5.3 (4.0) (4.3) 0.08-34. ≈ 14.0%
  • Counter et al. 2005 Nambija gold-mining 80 2.8b (2.0) (17.5) 1.0-135.0 <10%
  • aPercentage of the population with hair mercury levels higher than 10 μg/g. bGeometric mean.
  • and latitude data in geographic databases and using and the remaining 20% of these Brazilian studies are from
  • tation of the hair mercury levels found in this population selected randomly from the general population (Tables 1,
  • illustrating the studies that assessed health outcomes in Table 10), the study by Bastos et al. (2006) covered from
  • Table 2: Hair mercury levels in French Guyana
  • Studied River Location N Hg mean μg/g Range μg/g > 10 μg/ga Fish
  • BASAG Maroni Sinnamary 285 1.8 5%
  • Oyapok Lower Maroni River 740 1.7-3.6 2.4%
  • Fréry Maroni Cayodé, Twenké, 235 11.4 (4.2) 1.9-27.2 57.4% 20-317 g/day
  • Children 156 10.2b 79% 2 meals/day
  • aPercentage of the population with hair mercury levels higher than 10 μg/g. bGeometric mean.
  • covering almost the totality of the Maroni and Oyapok In Brazilian Amazonia (Figures 1, 3, 4; Tables 3, 4, 5) hair
  • In the Andean Amazonian regions (Figure 1; Table 1), Negro River basin (61,62) and at the lakes from the
  • mercury levels were found below 10 μg/g in Ecuador Amapá State (Figure 1; Tables 3, 4, 5) (63), with means
  • In French Guiana (Figure 2; Table 2), most study sites and Tocantins Rivers, both from Amerindian reservations
  • Table 3: Hair mercury levels in Brazilian River Basins, General Population
  • Study Location N Hg mean μg/g Range μ > 10 μg/ga Fish
  • Leino & Lodenius 1995 Tucuruí area 125 35.0 (29.0) 0.9-240.0 11 meals/week
  • The Tapajós and Madeira Rivers basins are not displayed in this table (see Tables 5, 6, 7, 8, 9, 10). aPercentage of the population with hair mercury
  • In the Tapajós River basin (Figure 3; Tables 6, 7, 8, 9) there urban or suburban areas (Santarém and Santana do Itu-
  • Table 4: Mercury levels in Brazilian River Basins, Target Groups
  • Studied population Location N Hg mean μg/g Range > 10 μg/ga Fish
  • Tavares Barão de Melgaço 114 2.1 (1.8) (1.4) 0.4-7.6 0% 4.6 meals/week
  • The Tapajós and Madeira Rivers basins are not displayed in this table (see Tables 5, 6, 7, 8, 9, 10). aPercentage of the population with hair mercury
  • lished in 1995 (77,80) showed much higher levels (means ally small and traditional riverside villages, some of them
  • lowing decade (mean = 8.6 μg/g and median = 8.0 μg/g) necting them to larger villages and cities. It is possible to
  • In the Madeira River basin (Figure 4; Table 10) most study because they are also farmers or hunters, even if fish
  • of them show these results (Tables 1, 2, 3, 4, 5, 6, 7, 8, 9, Juruti. The low hair mercury levels cannot be explained by
  • Table 5: Hair mercury levels in Brazilian River Basins, Occupational Groups
  • Study Location N Hg mean μg/g Range > 10 μg/ Fish

Methods (brief)

  • included studies with a direct measure of hair mercury concentrations in a sample size larger than
  • and citotoxic damages have been shown (30-33), as well Exclusion criteria were sample sizes less than 10 people,
  • ronmental Protection Agency (EPA) stated the Reference tables, showing author, study sites, sample sizes, hair mer-
  • named each study site on the map displaying a represen- studies. Several studies have used a large sample size,
  • represents a hair mercury measure and the target group the same basin. Some of them used smaller sample sizes,
  • the populations had sample sizes of less than 10 people,
  • River basins, with large sample sizes from the general pop- mercury levels are very variable between basins and study
  • Leino & Lodenius 1995 Tucuruí area 125 35.0 (29.0) 0.9-240.0 11 meals/week
  • (33,81). The sample sizes and study designs were very dif- hypothesize that this situation makes those populations
  • that year took samples of 10 and 48 people. In 2002, the In spite of those considerations, some populations with
  • and the studies published in 2002 and 2004 took samples 10 μg/g, even if there was a significant relation with fish
  • sume is collected from local lakes and minor rivers, and sue, finding positive relations between fish mercury con-
  • population were lower than those found in most central and human samples (13,52,58,63,96). In those studies,
    1. Leino T, Lodenius M: Human hair mercury levels in Tucurui 83. Barbosa AC, Silva SR, Dorea JG: Concentration of mercury in
  • mination of mercury and selenium in hair samples of Brazil- 88. Dolbec J, Mergler D, Larribe F, Roulet M, Lebel J, Lucotte M:
  • nium concentrations in hair samples of women in fertile age
  • samples from a gold mining area in the Amazon region of
  • cury in fish and hair samples from the Balbina Reservoir,

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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Verification notes

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  • Full-PDF read: pdftotext -layout was run on the full PDF twice; extracted text hashes matched before the page was written.
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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