Monitoring of occupational exposure to tetrachloroethene by analysis for unmetabolized tetrachloroethene in blood and urine in comparison with urinalysis for trichloroacetic acid
“…A similar calculation for XYLs (for which 50 ppm=217 mg/m 3 ) gave 1,085 lg/min for the lung absorption and 0.0531 lg/min for urinary excretion, and therefore a rate of 0.0049%. The two rates indicate that very minor portions of absorbed TOL and XYLs are excreted unmetabolized in urine, as is the case for chlorinated hydrocarbons such as methyl chloroform (Mizunuma et al 1995) and tetrachloroethylene (Furuki et al 2000). A similar result can be expected for EB because water solubility of EB is only slightly lower than that of XYLs (Table 6), but no quantitative estimation was made due to technical difficulties in obtaining necessary data as discussed above.…”
Section: Discussionsupporting
confidence: 54%
“…Among the biological materials, urine is of particular interest to this group (e.g., Mizunuma et al 1995;Kawai et al 1997;Furuki et al 2000) because the validity of toluene in urine as a toluene-exposure indicator is almost comparable with that in blood (Kawai et al 1996), and the collection of a urine sample is more readily accepted by the subject of examination than blood-sample drawing.…”
Biological monitoring of exposure by means of analysis of end-of-shift urine for mother solvent is possible, not only in the case of TOL as previously reported, but also in cases of XYLs, either for three isomers in combination or separately.
“…A similar calculation for XYLs (for which 50 ppm=217 mg/m 3 ) gave 1,085 lg/min for the lung absorption and 0.0531 lg/min for urinary excretion, and therefore a rate of 0.0049%. The two rates indicate that very minor portions of absorbed TOL and XYLs are excreted unmetabolized in urine, as is the case for chlorinated hydrocarbons such as methyl chloroform (Mizunuma et al 1995) and tetrachloroethylene (Furuki et al 2000). A similar result can be expected for EB because water solubility of EB is only slightly lower than that of XYLs (Table 6), but no quantitative estimation was made due to technical difficulties in obtaining necessary data as discussed above.…”
Section: Discussionsupporting
confidence: 54%
“…Among the biological materials, urine is of particular interest to this group (e.g., Mizunuma et al 1995;Kawai et al 1997;Furuki et al 2000) because the validity of toluene in urine as a toluene-exposure indicator is almost comparable with that in blood (Kawai et al 1996), and the collection of a urine sample is more readily accepted by the subject of examination than blood-sample drawing.…”
Biological monitoring of exposure by means of analysis of end-of-shift urine for mother solvent is possible, not only in the case of TOL as previously reported, but also in cases of XYLs, either for three isomers in combination or separately.
“…Residing near dry-cleaning facilities or storing recently dry-cleaned clothes at home can contribute to increased blood tetrachloroethene levels (Begerow et al, 1996;Popp et al, 1992). In contrast, tetrachloroethene blood levels in occupationally exposed workers have been reported to be many thousand times higher than the unexposed general population (Begerow et al, 1996;Furuki et al, 2000;Monster et al, 1983). The occupational biological exposure index associated with an 8-hour exposure of 25 ppm is 500 μg/L tetrachloroethene in blood (ACGIH, 2007).…”
“…Dichloromethane, chloroform and tetrachloroethene (also known also as tetrachloroethylene or perchloroethylene) are chlorinated hydrocarbon solvents widely employed in industry as degreasing agents 6) and are even more commonly used for the dry-cleaning of clothes 4,7,8) .…”
Chlorinated hydrocarbon solvents are often used for dry-cleaning clothes in the laundry industry. The object of this study was to monitor the occupational exposure of dry-clean employees coming into contact with VOXs. Twenty five workers collected their urine samples before the work shift, after 4 h of work and after the work shift. The analyses of urine samples and solvents used in dry-cleaning were performed using TLHS-DAI-GC-ECD. Chloroform was detected in all urine samples, and dichloromethane and tetrachloroethene in nearly all urine samples collected before and after the work shift. The concentrations of the compounds determined in urine samples were higher at the end of the workday in directly exposed individuals. Concentrations of the compounds determined in urine samples depended mainly on the type of activities carried out at the dry-cleaning establishments.
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