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MERCURY 249<br />

2. HEALTH EFFECTS<br />

The accumulation of mercury is greater in larger fish <strong>and</strong> in fish higher in the food chain. The tendency <strong>for</strong><br />

increased mercury concentration with increasing fish body weight is particularly noticeable in carnivorous<br />

fish species. Malm et al. (1995) analyzed mercury concentrations in 16 species of carnivorous fish from the<br />

Tapajos River basin in Brazil <strong>and</strong> hair samples from local populations who regularly ate such fish. Mercury<br />

levels in the fish averaged 0.55 ppm (range, 0.04–3.77 ppm), <strong>and</strong> the mercury levels in the hair of the<br />

affected fish-eating populations averaged approximately 25 ppm. In one population that consumed higher<br />

quantities of large carnivorous fish at the end of the local rainy season, 8 of 29 persons evaluated had hair<br />

mercury levels above 40 ppm, <strong>and</strong> one individual had a hair mercury concentration of 151 ppm. Some<br />

villages along the river can have per capita daily fish consumption rates around 200 g or more, which would<br />

greatly impact the human body burden <strong>and</strong> hair levels of mercury in such populations.<br />

Hair-to-Blood Concentration Ratio<br />

The hair:blood concentration ratio <strong>for</strong> total mercury is frequently cited as 250. However, a precise basis <strong>for</strong><br />

this particular value is unclear. Ratios reported in the literature range from 140 to 416, a difference of more<br />

than a factor of 2.5 (see Table 2-9). Differences in the location of hair sampled (head versus chest, distance<br />

of sample from head or skin) may contribute to differences in observed ratios between studies. For<br />

example, as much as a 3-fold seasonal variation in mercury levels was observed in average hair levels <strong>for</strong> a<br />

group of individuals with moderate-to-high fish consumption rates, with yearly highs occurring in the fall<br />

<strong>and</strong> early winter (Phelps et al. 1980; Suzuki et al. 1992). Thus, it is important to obtain hair samples as<br />

close to the follicle as possible to obtain an estimate of recent blood levels. Large errors (the direction of<br />

which depends on whether samples were taken while blood levels were falling or rising) could result if hair<br />

samples are not taken close to the scalp. Several studies did not report the distance to the scalp <strong>for</strong> the hair<br />

samples taken. The high slope reported by Tsubaki (1971a) may have reflected the fact that mercury levels<br />

were declining at the time of sampling (Berglund et al. 1971), so the hair levels may reflect earlier, higher<br />

blood levels. Hair taken from different parts of the body also may yield different ratios. In 26 subjects with<br />

moderate-to-high fish consumption, axillary hair (i.e., from the armpit area) was found to contain an<br />

average of 23% less mercury than head hair (Skerfving et al. 1974).<br />

Phelps et al. (1980) obtained multiple blood samples <strong>and</strong> sequentially analyzed lengths of hair from<br />

339 individuals in Northwestern Ontario. The large sample size <strong>and</strong> the attention to sampling <strong>and</strong> analysis<br />

with regard to the hair:blood relationship make the results from this study the most appropriate to use <strong>for</strong><br />

estimating the mercury blood levels of the Seychellois women during pregnancy. The actual ratio Phelps et

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