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MERCURY 353<br />

2. HEALTH EFFECTS<br />

unknown. This in<strong>for</strong>mation is needed to design better treatment drugs <strong>and</strong> protocols. Mechanistic studies<br />

are needed on how mercury (in its various <strong>for</strong>ms) is excreted <strong>and</strong> how such activities can be enhanced.<br />

An important priority research <strong>and</strong> data need is a study of the effects of dietary selenium on the absorption<br />

<strong>and</strong> toxicity of methylmercury. Primates would be the most appropriate species <strong>for</strong> such a study. Oral<br />

dosage levels (in food) should cover an sufficient dose range to provide useful in<strong>for</strong>mation <strong>for</strong> high fish<br />

consuming populations. Mercury excretion should also be measured <strong>and</strong> compared with controls at least<br />

weekly, with the entire study length being not less than 6 months, <strong>and</strong> preferably one to two years in<br />

duration. Concurrent neurobehavioral testing should be included, if possible, <strong>and</strong> be conducted at fixed<br />

intervals depending upon the duration of the study.<br />

Comparative <strong>Toxic</strong>okinetics. There is only limited data available on species differences in<br />

absorption rates following oral exposures to all <strong>for</strong>ms of mercury, <strong>and</strong> the results are negative (i.e., no<br />

differences) (Clarkson 1971, 1972a; Friberg <strong>and</strong> Nordberg 1973; Nielsen <strong>and</strong> Andersen 1990; Rice<br />

1989b). There are data concerning inhalation absorption of metallic <strong>and</strong> inorganic mercury (Berlin et al.<br />

1969; Cherian et al. 1978; Clarkson 1989; Hursh et al. 1976); however, the data are insufficient to allow<br />

<strong>for</strong> interspecies comparisons (Ostlund 1969). Studies comparing the inhalation absorption of all <strong>for</strong>ms of<br />

mercury in humans <strong>and</strong> animals are needed to improve the utility of animal data in assessing human risk.<br />

The limited in<strong>for</strong>mation available on dermal exposure suggests that dermal absorption of both inorganic<br />

<strong>and</strong> organic mercury compounds occurs in humans <strong>and</strong> animals, although no comparison of the rate or<br />

extent of absorption can be made between species (Gotelli et al. 1985; Hursh et al. 1989; Laug <strong>and</strong> Kunze<br />

1949; Schamberg et al. 1918). As with inhalation exposure, studies comparing the dermal absorption of all<br />

<strong>for</strong>ms of mercury in humans <strong>and</strong> animals are needed to improve the utility of animal data <strong>for</strong> assessing<br />

human risk.<br />

The distribution of mercury in humans <strong>and</strong> animals appears to be similar. The lipophilic nature of metallic<br />

mercury results in its distribution throughout the body in humans (Takahata et al. 1970) <strong>and</strong> in animals<br />

(Berlin <strong>and</strong> Johansson 1964; Berlin et al. 1966). Distribution of inorganic mercury compounds resembles<br />

that of metallic mercury; however, human distribution is preferentially to the kidneys, liver, <strong>and</strong> intestines.<br />

Also, levels in the brain are substantially lower, as these compounds have a lower lipophilicity.<br />

Distribution of organic mercury compounds is also similar to that of metallic mercury. The ability of<br />

methylmercuric compounds to cross the blood-brain <strong>and</strong> placental barriers enables ready distribution to all<br />

tissues, although, again, the highest levels are found in the kidneys. Phenylmercuric compounds are

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