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MERCURY 347<br />

2. HEALTH EFFECTS<br />

needed to evaluate the potential developmental toxicity of inorganic mercury to populations, specifically<br />

young children, living near hazardous waste sites. Longitudinal studies <strong>for</strong> higher dose level acute <strong>and</strong><br />

intermediate exposures are needed to determine the potential delayed expression of toxicity.<br />

Prenatal exposure to methylmercury from contaminated food during the early stages of pregnancy has<br />

caused neurological damage in humans (Amin-Zaki et al. 1974; Bakir et al. 1973; Choi et al. 1978; Cox et<br />

al. 1989; Engleson <strong>and</strong> Herner 1952; Harada 1978; Marsh et al. 1980, 1981, 1987; Matsumoto et al. 1965;<br />

McKeown-Eyssen et al. 1983; Snyder <strong>and</strong> Seelinger 1976). Severe neurological impairment developed in<br />

a child exposed in utero to methylmercury, <strong>and</strong> effects were still present at 6 years of age (Snyder <strong>and</strong><br />

Seelinger 1976). In animals, numerous oral exposure studies on the developmental effects of organic<br />

mercury have been conducted. Disruptions in the development of the nervous system in rats, mice,<br />

hamsters, <strong>and</strong> guinea pigs (Chang et al. 1977; Inouye <strong>and</strong> Kajiwara 1988; Khera <strong>and</strong> Tabacova 1973;<br />

Reuhl et al. 1981a, 1981b) <strong>and</strong> in the immune system in rats (Ilback et al. 1991) have been reported.<br />

Behavioral changes were also observed in rats <strong>and</strong> mice (Bornhausen et al. 1980; Hughes <strong>and</strong> Annau<br />

1976; Olson <strong>and</strong> Boush 1975). Additional long-term inhalation, oral, <strong>and</strong> dermal studies <strong>for</strong> inorganic<br />

<strong>and</strong> organic mercury are needed to evaluate the threshold of developmental effects in workers chronically<br />

exposed to mercury or in populations living near hazardous waste sites.<br />

Immunotoxicity. The results from two occupational studies indicate a decreased serum IgG levels in<br />

workers to inhaled metallic mercury vapors (Bencko et al. 1990; Moszczynski et al. 1990b), but these studies<br />

are limited <strong>and</strong> did not evaluate potential confounders (smoking <strong>and</strong> alcohol). Other studies in similarly<br />

exposed populations did not observe an increases in serum immunoglobulins (IgA, IgG, IgE, or IgM) <strong>and</strong><br />

autoantibody titres (antilaminin or antiglomerular basement membrane antibodies) (Bernard et al. 1987;<br />

Cardenas et al. 1993; Langworth et al. 1992b). There is limited in<strong>for</strong>mation in humans that suggests that<br />

certain individuals may develop an autoimmune response (Tubbs et al. 1982; Moszczynski et al. 1995).<br />

Data on immunological effects following oral exposure to organic mercury compounds in humans are not<br />

available. Oral exposures to inorganic <strong>and</strong> organic mercury in animals indicate that the immune system may<br />

be a target organ <strong>for</strong> mercury. Immune deposits were observed in the intestines <strong>and</strong> kidneys of rats exposed<br />

to mercuric chloride <strong>for</strong> 2 months, but no functional changes were evident in these tissues (Andres 1984).<br />

Suppression of the lymphoproliferative response occurred at a higher dose of mercury in mice exposed to<br />

mercuric chloride <strong>for</strong> 7 weeks (Dieter et al. 1983). Reduced natural killer cell activity in spleen <strong>and</strong> blood<br />

was exhibited in mice administered a diet containing methylmercury <strong>for</strong> 12 weeks (Ilback 1991). It is<br />

unknown how an adverse effect on the immune system from exposure to one <strong>for</strong>m of mercury

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