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MERCURY 331<br />

2. HEALTH EFFECTS<br />

groups) have been used to decrease the absorption rate of methylmercury (Clarkson et al. 1973). The oral<br />

administration of activated charcoal has also been suggested (Gossel <strong>and</strong> Bricker 1984; Stutz <strong>and</strong> Janusz<br />

1988). Rapid removal of mercury from the gastrointestinal tract may be indicated in some acute, highdose<br />

situations. In such situations, immediate emesis or gastric lavage has been suggested (Goldfrank et<br />

al. 1990; Haddad <strong>and</strong> Winchester 1990). Inclusion of salt-poor albumin or sodium <strong>for</strong>maldehyde<br />

sulfoxylate in the lavage fluid to convert the mercuric ion into the less soluble mercurous ion in the<br />

stomach has also been recommended (Haddad <strong>and</strong> Winchester 1990). Emesis is contraindicated<br />

following the ingestion of mercuric oxide, presumably because of the risk of damage to the esophagus as<br />

the potentially caustic compound is ejected. A saline cathartic, such as magnesium sulfate, to speed<br />

removal from the gastrointestinal tract has also been recommended unless diarrhea has already begun<br />

(Haddad <strong>and</strong> Winchester 1990; Stutz <strong>and</strong> Janusz 1988). Giving CaNa2-EDTA is contraindicated because<br />

it binds poorly to mercury, may be toxic to the kidneys, chelates other essential minerals, <strong>and</strong> may cause<br />

redistribution of mercury in the body (Gossel <strong>and</strong> Bricker 1984).<br />

2.10.2 Reducing Body Burden<br />

Since the main source of mercury exposure <strong>for</strong> the general public is organic mercury in the diet,<br />

minimizing the consumption of mercury-laden fish <strong>and</strong> shellfish is an effective means of reducing the<br />

body burden. The amount of inhaled mercury vapor from accidental spills of metallic mercury (e.g., from<br />

broken thermometers or electrical switches) can be minimized by in<strong>for</strong>ming the general public of the<br />

potential dangers <strong>and</strong> volatility of liquid mercury, <strong>and</strong> by prompt <strong>and</strong> thorough clean-up of liquid mercury<br />

spills.<br />

Following exposure <strong>and</strong> absorption, metallic mercury is distributed primarily to the kidneys. Elemental<br />

mercury is highly soluble in lipids <strong>and</strong> easily crosses cell membranes (Gossel <strong>and</strong> Bricker 1984),<br />

particularly those of the alveoli (Florentine <strong>and</strong> Sanfilippo 1991). Once in the blood, this <strong>for</strong>m of<br />

mercury can distribute throughout the body, as well as penetrate the blood-brain barrier, thus<br />

accumulating in the brain (Berlin et al. 1969). The body burden half-life of metallic mercury is about<br />

1–2 months (Clarkson 1989). The kidney is also the primary organ of accumulation <strong>for</strong> compounds of<br />

inorganic mercury, but the liver, spleen, bone marrow, red blood cells, intestine, <strong>and</strong> respiratory mucosa<br />

are target tissues as well (Haddad <strong>and</strong> Winchester 1990; Rothstein <strong>and</strong> Hayes 1964). Inorganic mercury<br />

is excreted primarily through the kidneys; its half-life ranges from 42–60 days (Hursh et al. 1976; Rahola<br />

et al. 1973). As with elemental mercury, organic mercury compounds accumulate throughout the body<br />

(Aberg et al. 1969; Miettinen 1973). Accumulation of organic mercury also occurs in the liver, where it

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