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MERCURY 430<br />

5. POTENTIAL FOR HUMAN EXPOSURE<br />

conducted another study to assess the migration of several toxic metals from crayons, watercolor paints, <strong>and</strong><br />

water-based paints. Migration of mercury from the art materials was determined by scraping flakes of the<br />

products into dichloromethane <strong>for</strong> 2 hours at 54E C. The degreased material was then placed in an aqueous<br />

HCl solution, shaken, <strong>and</strong> centrifuged. The supernatant was then filtered through a 0.45 µ membrane filter<br />

<strong>and</strong> was analyzed. These authors reported that the migration of mercury from these art supplies was<br />

0.24–5.98 ppm <strong>for</strong> red, 0.26–3.63 ppm <strong>for</strong> blue, 0.20–4.79 ppm <strong>for</strong> yellow, 0.22–5.68 ppm <strong>for</strong> green, <strong>and</strong><br />

0.17–3.63 ppm <strong>for</strong> white paint. Migration of mercury from the product occurred in 57% of the samples<br />

tested. The migration limit set by European St<strong>and</strong>ard EN71-3 <strong>for</strong> mercury is 60 ppm. This value was not<br />

exceeded in any of the art supplies tested. The authors, however, believe that children might be exposed<br />

not only to mercury, but to several other metals that also co-migrated from the paints.<br />

Cigarettes. In a study conducted in West Germany, Pesch et al. (1992) analyzed mercury concentrations<br />

in 50 br<strong>and</strong>s of cigarettes manufactured in 2 Western <strong>and</strong> 6 Eastern European countries. These authors<br />

reported that in 1987, the average mercury concentration detected in cigarettes was 0.098 µg/g (ppm) (dry<br />

weight) (range, 0.06 to 0.14 ppm dry weight). In 1991, the mean mercury concentrations <strong>for</strong> cigarettes<br />

were 0.034 µg/g (ppm) dry weight (range, 0.007–0.092 ppm dry weight) <strong>for</strong> Eastern Europe <strong>and</strong> 0.015 µg/g<br />

(ppm) dry weight (range, 0.006–0.037 ppm dry weight) <strong>for</strong> Western European countries. The authors<br />

attributed the decline in mercury content of cigarettes to environmental protection measures instituted in the<br />

intervening years (Pesch et al. 1992).<br />

Religious <strong>and</strong> Ethnic Rituals, Ceremonies, <strong>and</strong> Practices. While some of medicinal <strong>and</strong><br />

pharmaceutical uses of mercury compounds have been replaced in recent years, individuals in some ethnic<br />

or religious groups may still use mercury in various religious or ethnic rituals, practices, <strong>and</strong> ceremonies<br />

that can expose them to elevated mercury concentrations in room air. Metallic mercury has been used in<br />

Latin American <strong>and</strong> Caribbean communities as part of certain religious practices (e.g., Voodoo, Santeria,<br />

<strong>and</strong> Espiritismo), predominantly in domestic settings (Wendroff 1990). This use of mercury can<br />

contaminate a dwelling or automobile if the mercury is not completely removed from flooring, carpeting,<br />

<strong>and</strong> woodwork in an appropriate manner. Metallic mercury (sometimes under the name azogue) currently is<br />

sold in shops called botanicas which stock medicinal plants, traditional medicines, incense, c<strong>and</strong>les, <strong>and</strong><br />

perfumes. Botanicas typically dispense mercury in gelatin capsules or sometimes in small glass vials.<br />

Some religious practices involve sprinkling metallic mercury on the floor of the dwelling or of a car, mixing<br />

metallic mercury with soap <strong>and</strong> water to wash the floor, or placing it in an open container to rid the house of<br />

evil spirits. Other practices involve carrying a small amount of mercury in a vial on the person, or mixing

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