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MERCURY 144<br />

2. HEALTH EFFECTS<br />

adverse developmental effects associated with prenatal <strong>and</strong> postnatal exposure to methylmercury in fish at<br />

the levels experienced in this cohort. The actual exposure is reflected in a mean maternal hair level of<br />

6.8 ppm <strong>for</strong> the prenatal exposure (SD=4.5, n=711, range, 0.5-26.7) <strong>and</strong> in a mean children’s hair level of<br />

6.5 ppm (SD=3.3, n=708, range, 0.9-25.8) <strong>for</strong> both the prenatal <strong>and</strong> subsequent postnatal exposure. The<br />

age-appropriate main outcome measures included: (1) the McCarthy Scales of Children’s Abilities, (2) the<br />

Preschool Language Scale, (3) the Woodcock-Johnson Tests of Achievement—Letter <strong>and</strong> Word<br />

Recognition, (4) Woodcock-Johnson Tests of Achievement—Applied Problems <strong>and</strong>, (5) the Bender Gestalt<br />

test, <strong>and</strong> (6) the Child Behavior Checklist. The test results were similar to what would be expected from a<br />

healthy, well-developing U.S. population. No test indicated a deleterious effect of methylmercury from the<br />

exposure levels received in this population. Four of the six measures showed better scores in the highest<br />

MeHg groups compared with lower groups <strong>for</strong> both prenatal <strong>and</strong> postnatal exposure. The authors conclude<br />

that this result is likely due to the benefits of increased levels of fish in the diet, possibly because of<br />

increased consumption of omega-3-fatty acids. Serum from a subset of 49 of the children was sampled <strong>for</strong><br />

polychlorinated biphenyl (PCB) levels. None of the samples had detectable levels (detection limit<br />

0.2 ng/mL) <strong>for</strong> any of the 28 congeners assayed (from congener 28 to 206), indicating that was no<br />

concurrent (i.e, potentially confounding) exposure to PCBs in this population. The median level of total<br />

mercury <strong>for</strong> each of 25 species sampled was 0.004–0.75 ppm, with most medians in the range of<br />

0.05–0.25 ppm, levels that are comparable to fish in the U.S. market. The authors conclude, that this most<br />

recent NOAEL of 6.8 ppm <strong>for</strong> the SCDS cohort at 66 months of age strongly supports the findings at earlier<br />

ages, <strong>and</strong> that the benefits of eating fish outweigh the small risk of adverse effects from an increased<br />

exposure to methylmercury <strong>for</strong> this exposure pathway.<br />

Weihe et al. (1996) began a long-term evaluation of the health implications <strong>for</strong> people living in the Faroe<br />

Isl<strong>and</strong>s who are exposed to heavy metals <strong>and</strong> polychlorinated biphenyls (PCBs) from the consumption of<br />

fish <strong>and</strong> pilot whales. A birth cohort of 1,000 children was examined at approximately 7 years of age <strong>for</strong><br />

neurobehavioral dysfunctions associated with prenatal exposure to mercury <strong>and</strong> PCB. Preliminary analyses<br />

of the data show that several neurobehavioral tests are associated with mercury exposure parameters. With<br />

emphasis on prenatal exposures to PCB, another cohort was generated during 1994–1995, <strong>and</strong> this cohort<br />

will be followed closely during the next years. In the Faroe Isl<strong>and</strong>s, marine food constitutes a considerable<br />

part of the diet. In addition to fish, both meat <strong>and</strong> blubber from pilot whales are included in the diet. Muscle<br />

tissue of pilot whales caught in the Faroe Isl<strong>and</strong>s contains an average mercury concentration of 3.3 µg/g<br />

(16 nmol/g), about half of which is methylmercury. In some years an evenly distributed annual catch of<br />

pilot whales would make the average dietary intake of mercury close to more than the Provisional

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