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Mean air concentrations during the day on workdays (HTO 10.3 Bq/m3, HT 5.8 Bq/m3) were higher than at other times (0.7 2.6 Bq/m3).
For both CHCl3 and BDCM, the normalized mean air concentrations were much greater for the showering activity than for the bathing activity.
Increases in monosomy 5 and 7; trisomy 1, 7, 8, and 21; and aneuploidy of chromosome X and t 8, 21) have been reported in lymphocytes of workers exposed to benzene at mean air concentrations of approximately 30 45 ppm compared with unexposed groups (Smith et al. 1998; Zhang et al. 1998, 2002, 2005).
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Regional mean air pollution concentrations were extrapolated by creating air pollution concentration interpolation maps (16).
The mean personal air concentrations of DBP, di-isobutyl phthalate, and DEHP are higher in Krakow, whereas the mean personal air concentration of DEP is higher in New York.
Table 2 presents the distributions of the monthly mean air pollutant concentrations during the study period.
We considered mean air pollution concentrations on the same day and lags of 1, 2, and 3 days.
Therefore, in this article we report only the effects of 2-day running mean air pollution concentrations.
The range of annual mean air pollutant concentrations for each quintile can be found in Supplementary Appendix online.
Table 2 presents the distributions of the monthly mean air pollutant concentrations during the first 3 months pregnancy.
In our sample, two homes with residents with positive bioassays had mean air mercury concentrations between 1 and 5 μg/m.
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