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MERCURY 452<br />

5. POTENTIAL FOR HUMAN EXPOSURE<br />

Naleway et al. (1991) reported results of a screening study conducted in 1985 <strong>and</strong> 1986 by the American<br />

Dental Association to analyze urinary mercury concentrations in dentists <strong>and</strong> identify those individuals with<br />

elevated urinary mercury levels. In 1985, 1,042 U.S. dentists were screened, <strong>and</strong> a mean urinary mercury<br />

level of 5.8 µg/L (ppb) (maximum 84 µg/L) was reported. In 1986, 772 dentists screened had a mean<br />

urinary level of 7.6 µg/L (ppb) (maximum 115 µg/L). Their mean urinary mercury levels were substantially<br />

lower than pooled data (mean, 14.2 µg/L) from dentists participating in the screening program from<br />

1975–1983 (Naleway et al. 1985). The authors noted a substantial decline, particularly during the last 5<br />

years (1982–1986), which was attributed to better mercury hygiene <strong>and</strong> the reduced use of amalgam<br />

restorations. This study also evaluated responses from a questionnaire survey of 480 dentists. The results<br />

indicated that those dentists reporting skin contact with mercury amalgam had mean urinary mercury levels<br />

of 10.4 µg/L (ppb), compared to 6.3 µg/L (ppb) in dentists reporting no skin contact; this difference was<br />

found to be statistically significant. Similarly, the mean urinary mercury level in dentists reporting mercury<br />

spills in the office was 7.8 µg/L (ppb), compared to 6.0 µg/L (ppb) <strong>for</strong> those reporting no mercury spills.<br />

Again, the difference was significant. Additionally, the number of hours practiced per week was found to<br />

weakly correlate with urinary mercury concentrations (Naleway et al. 1991).<br />

Painters are another group that may be occupationally exposed to mercury vapors from volatilization of<br />

mercury during application of paint containing phenylmercuric acetate. Hefflin et al. (1993) studied the<br />

extent of mercury exposure from the application of exterior latex paints. These authors compared the air <strong>and</strong><br />

urinary mercury concentrations of 13 professional male painters with those of 29 men having other<br />

occupations (nonpainters). The painters applied 2 br<strong>and</strong>s of exterior latex paint that contained mercury; the<br />

median concentration was 570 mg/L (ppm). The median air mercury concentration was higher <strong>for</strong> painters<br />

(1.0 µg/m 3 ; range, non-detectable to 4 µg/m3 ) than <strong>for</strong> nonpainters (non-detected; range, not detected to<br />

3 µg/m3 ). The median urinary mercury concentration was nearly twice as high <strong>for</strong> painters (9.7 µg/L [ppb];<br />

range, 5.9–20.4 µg/L) as <strong>for</strong> nonpainters (5.0 µg/L [ppb]); range, 2.6–11.6 µg/L [ppb]) (p=0.0001). The<br />

normal range of urinary mercury is

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