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MERCURY 354<br />

2. HEALTH EFFECTS<br />

initially distributed in a similar manner to methylmercury; however, the distribution eventually resembles<br />

that of inorganic mercury.<br />

The available evidence suggests that feces <strong>and</strong> urine constitute the main excretory pathways of metallic<br />

mercury <strong>and</strong> inorganic mercury compounds in both humans <strong>and</strong> animals. Additional excretory routes<br />

following metallic <strong>and</strong> inorganic mercury exposure include exhalation <strong>and</strong> secretion in saliva, sweat, bile,<br />

<strong>and</strong> breast milk (Joselow et al. 1968b; Lovejoy et al. 1974; Rothstein <strong>and</strong> Hayes 1964; Sundberg <strong>and</strong><br />

Oskarsson 1992; Yoshida et al. 1992). Excretion following exposure to organic mercury is considered to<br />

be predominantly through the fecal route in humans. Evidence from studies in humans <strong>and</strong> animals (mice,<br />

rats) suggests that exposure to methylmercury leads primarily to biliary secretion, while excretion is<br />

initially through the bile; it then shifts to the urine following phenylmercury exposure (Berlin <strong>and</strong> Ullberg<br />

1963; Berlin et al. 1975; Gotelli et al. 1985; Norseth <strong>and</strong> Clarkson 1971). No further comparative studies<br />

on excretion are warranted because there is no apparent difference in the excretion of mercury in any <strong>for</strong>m<br />

in humans <strong>and</strong> animals.<br />

Two PBPK models have recently been published on the pharmacokinetics of methylmercury in rats (Farris<br />

et al. 1993; Gray 1995). Additional PBPK studies are needed to support species <strong>and</strong> dose extrapolations,<br />

<strong>and</strong> a better underst<strong>and</strong>ing of the underlying toxic <strong>and</strong> kinetic mechanisms is needed in support of human<br />

risk assessments.<br />

Validation of in vitro data is a major need. Much of the data from in vitro experimentation is based on<br />

unrealistic concentrations of the toxicant or is derived from studies using non-physiological designs. In<br />

particular, more validation is needed <strong>for</strong> immunotoxicity studies <strong>and</strong> biochemical studies.<br />

Methods <strong>for</strong> Reducing <strong>Toxic</strong> Effects. Nonspecific methods or treatments <strong>for</strong> reducing absorption<br />

following mercury exposure include the administration of chelators or protein solutions to neutralize <strong>and</strong><br />

bind to inorganic mercury compounds (Bronstein <strong>and</strong> Currance 1988; Florentine <strong>and</strong> Sanfilippo 1991;<br />

Gossel <strong>and</strong> Bricker 1984). The use of a particular chelator is dependent upon the type of mercury<br />

exposure (Gossel <strong>and</strong> Bricker 1984). Chelation therapy is the treatment of choice <strong>for</strong> reducing the body<br />

burden of mercury (Florentine <strong>and</strong> Sanfilippo 1991; Gossel <strong>and</strong> Bricker 1984; Haddad <strong>and</strong> Winchester<br />

1990). However, chelation releases mercury from soft tissues that can then be redistributed to the brain.<br />

Additional research is needed to elucidate the mechanisms of absorption <strong>and</strong> distribution of inorganic <strong>and</strong><br />

organic mercury. Animal studies suggest that antioxidants may be useful <strong>for</strong> decreasing the toxicity of

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