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MERCURY<br />

2. HEALTH EFFECTS<br />

coordination <strong>and</strong> memory showed no significant deficits in the exposed group. The exposed <strong>and</strong> control<br />

groups were matched <strong>for</strong> age, sex, vocational status, education, <strong>and</strong> mean number of amalgam fillings. A<br />

group-average exposure concentration of 0.025 mg/m 3 mercury vapors was estimated from repeated<br />

analyses of blood mercury concentration (mean, 51.3 nmol/L .10 µg/L) (see the discussion regarding these<br />

estimated exposure levels in Section 2.5). Also, no effects on tremors, bimanual coordination, color<br />

determination, or reaction time were observed in chloralkali workers with more than 7 years of exposure to<br />

low levels of mercury; ambient air levels measured <strong>for</strong> 2 years prior to testing averaged 0.076 mg/m 3 <strong>and</strong><br />

the average blood level in the workers was 19.9 µg/L (Schuckmann 1979). Negative findings were also<br />

noted when the results of tremor frequency spectra <strong>and</strong> psychometric tests of a group of chloralkali workers<br />

exposed <strong>for</strong> an average of 13.5 years were compared to unexposed controls (Langworth et al. 1992a). The<br />

TWA exposure level was estimated to be 0.025 mg/m 3 , based on measurements taken at the time of the<br />

study, <strong>and</strong> blood levels in the workers averaged 55 nmol/L (.11 µg/L). Despite the negative objective<br />

findings, subjective reports of fatigue, memory disturbances, <strong>and</strong> confusion were significantly higher in the<br />

exposed workers.<br />

Boogaard et al. (1996) evaluated the effects of exposure to elemental mercury on the nervous system <strong>and</strong><br />

the kidneys of workers producing natural gas in the Netherl<strong>and</strong>s. Early signs of alterations in renal <strong>and</strong><br />

neurological functions were studied in three groups of workers who were exposed to different levels of<br />

mercury that were below the current ACGIH biological exposure index of 35 µg/g creatinine. Air<br />

concentrations ranged from 10 to 1,500 µg/m 3 (median, 67) at locations where mercury exposure was<br />

anticipated; the potential 8-hour TWA exposure ranged from 33 to 781 µg/m 3 (median, 88). Air<br />

concentrations ranged from 0 to 6 µg/m 3 at locations where little mercury exposure was expected. Current<br />

mercury concentrations in urine were 23.7, 4.1, <strong>and</strong> 2.4 µg/g in high, low, <strong>and</strong> control exposure groups,<br />

respectively; mercury concentrations in blood were 3.5, 1.5, <strong>and</strong> 2.2 µg/L, respectively. There were no<br />

differences among the three study groups with respect to either motor nerve conduction velocity or tremor<br />

frequency spectra of physiological tremors. Also, no significant correlations were found between the<br />

results of the neurological tests <strong>and</strong> any of the present or historical biological monitoring data.<br />

In contrast to the negative findings above, several studies have shown significant effects on tremor or on<br />

cognitive skills at comparable or lower group-average exposure levels (0.014–0.076 mg/m 3 ). Using the<br />

same paradigm as Langworth et al. (1992a), a significant difference was seen in the tremor frequency<br />

spectra in mercury-exposed workers from three industries who were exposed to low levels of mercury <strong>for</strong><br />

an average of 15.3 years (range, 1–41 years) when compared to unexposed controls (Fawer et al. 1983).<br />

62

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