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MERCURY 263<br />

2. HEALTH EFFECTS<br />

exposure to only a few drops of dimethylmercury is striking example of the danger of these <strong>for</strong>ms of organic<br />

mercury (Blayney et al. 1997; Nierenberg et al. 1998). At least 5 other deaths have been reported due to alkyl<br />

mercury exposure since its first synthesis in the mid-19th century (Toribara et al. 1997). These accidental<br />

poisoning cases also reveal a latency period of some months between the exposure <strong>and</strong> the onset of<br />

symptoms. In such cases, irreversible brain damage has already occurred by the time the first symptoms<br />

appeared.<br />

No in<strong>for</strong>mation was located regarding specific concentrations of elemental mercury vapor that may be lethal;<br />

however, lethal exposures have generally occurred as a result of exposure under conditions in which exposure<br />

levels are likely to be quite high (e.g., heating metallic mercury in a closed space). Death in these cases has<br />

generally been attributed to respiratory failure (Campbell 1948; Kanluen <strong>and</strong> Gottlieb 1991; Matthes et al.<br />

1958; Rowens et al. 1991; Soni et al. 1992; Taueg et al. 1992; Teng <strong>and</strong> Brennan 1959; Tennant et al. 1961).<br />

Deaths resulting from inhalation exposure to organic mercury compounds have also been reported (Brown<br />

1954; Hill 1943; Hook et al. 1954; Lundgren <strong>and</strong> Swensson 1949). Although the cause of death following<br />

inhalation of organic mercury was not reported, severe neurological dysfunction was observed prior to death.<br />

Lethal doses <strong>for</strong> acute oral exposure to inorganic mercury have been estimated to be 29–50 mg Hg/kg (Troen<br />

et al. 1951). Deaths resulting from oral exposure to inorganic mercury have been attributed to renal failure,<br />

cardiovascular collapse, <strong>and</strong> severe gastrointestinal damage (Gleason et al. 1957; Kang-Yum <strong>and</strong> Oransky<br />

1992; Troen et al. 1951).<br />

Deaths from consumption of methylmercury-contaminated foods are well documented in outbreaks in Japan<br />

<strong>and</strong> Iraq, <strong>and</strong> lethal doses of 10–60 mg Hg/kg have been estimated from tissue concentrations (Bakir et al.<br />

1973; Tsubaki <strong>and</strong> Takahashi 1986). Fatalities were attributed to central nervous system toxicity (Bakir et al.<br />

1973; Tamashiro et al. 1984). Pneumonia <strong>and</strong> nonischemic heart disease were prominent secondary causes of<br />

death in the Japan epidemic (Tamashiro et al. 1984). Case reports of deaths associated solely with dermal<br />

mercury exposure to inorganic mercury are limited to a woman who died after inserting a mercuric chloride<br />

tablet into her vagina (Millar 1916) <strong>and</strong> a man who died after a 2-month treatment with a topical medicine<br />

containing mercurous chloride (Kang-Yum <strong>and</strong> Oransky 1992). Death was attributed to renal failure in one<br />

of these cases (Kang-Yum <strong>and</strong> Oransky 1992), <strong>and</strong> severe renal damage was noted at the autopsy in the other<br />

(Millar 1916).

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