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MERCURY 281<br />

2. HEALTH EFFECTS<br />

concentration resulting from injection of mercuric chloride. Furthermore, the authors reported that metallic<br />

mercury appeared to oxidize to Hg +2 in the fetal tissues. Evidence that inhalation exposure may result in<br />

developmental toxicity comes from a study in which neonatal rats were exposed to metallic mercury vapor<br />

during a period of rapid brain development (this occurs postnatally in rodents but prenatally in humans),<br />

resulting in impaired spatial learning (Fredriksson et al. 1992). Oral administration of inorganic mercury<br />

salts to pregnant hamsters has been observed to produce an increase in the number of resorptions <strong>and</strong> small<br />

<strong>and</strong> edematous embryos (Gale 1974). Mercury-induced embryotoxicity in one non-inbred <strong>and</strong> five inbred<br />

stains of female hamsters was investigated by Gale <strong>and</strong> Ferm (1971). A single subcutaneous injection of<br />

9.5 mg Hg/kg as mercuric acetate to dams on Gd 8 produced a variety of mal<strong>for</strong>mations, including cleft<br />

palate, hydrocephalus, <strong>and</strong> heart defects, <strong>and</strong> statistically significant interstrain differences in the<br />

embryotoxic response. Single doses of 1.3–2.5 mg Hg/kg as mercuric acetate injected intravenously into<br />

pregnant hamsters on Gd 8 produced growth retardation <strong>and</strong> edema of the fetuses at all 3 dose levels, while<br />

an increase in the number of abnormalities was detected at the two higher doses (Gale <strong>and</strong> Ferm 1971). The<br />

relative effectiveness of different exposure routes in hamsters was compared by Gale (1974). The following<br />

sequence of decreasing efficacy was noted <strong>for</strong> mercuric acetate: intraperitoneal > intravenous ><br />

subcutaneous > oral. The lowest doses used (2 mg/kg <strong>for</strong> intraperitoneal <strong>and</strong> 4 mg/kg <strong>for</strong> the other 3 routes)<br />

were all effective in causing increased resorption <strong>and</strong> an increased percentage of abnormalities. Intravenous<br />

injection of 1.5 mg Hg/kg/day as mercuric chloride also resulted in a significant increase in the number of<br />

abnormal preimplantation embryos (Kajiwara <strong>and</strong> Inouye 1986).<br />

In animals, embryolethal, anatomical, <strong>and</strong> behavioral effects have been reported following oral exposure of<br />

pregnant dams to methylmercury (Bornhausen et al. 1980; Cagiano et al. 1990; Elsner 1991; Fowler <strong>and</strong><br />

Woods 1977; Fuyuta et al. 1978, 1979; Guidetti et al. 1992; Gunderson et al. 1988; Hughes <strong>and</strong> Annau 1976;<br />

Ilback et al. 1991; Inouye <strong>and</strong> Kajiwara 1988; Inouye <strong>and</strong> Murakami 1975; Inouye et al. 1985; Khera <strong>and</strong><br />

Tabacova 1973; Lindstrom et al. 1991; Nolen et al. 1972; Olson <strong>and</strong> Boush 1975; Reuhl et al. 1981a, 1981b;<br />

Rice 1992; Rice <strong>and</strong> Gilbert 1990; Stoltenburg-Didinger <strong>and</strong> Markwort 1990; Yasuda et al. 1985). Thus far,<br />

the most sensitive animal assay <strong>for</strong> developmental neurotoxicity has been a behavioral paradigm that<br />

examined the number of rewarded responses to differential rein<strong>for</strong>cement at high rates (Bornhausen et al.<br />

1980). At doses of 0.008 mg Hg/kg/day <strong>and</strong> above, a dose-related decrease in rewarded responses was<br />

observed in 4-month-old offspring of rats treated on Gd 6–9. The effect was more pronounced in male<br />

offspring than females. Foster mothers were used to preclude consumption of contaminated milk during<br />

lactation.

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