2005). Overall, the levels of inhalable dust seems to have declined by 4% per year since 1975 in compounding, mixing and pre-treatment departments which often are male-dominated in Sweden (de Vocht et al. 2007a, b), but no decline was observed in curing departments during the 1990s. For post-treating departments, where many women are employed, there were no data to allow modeling of exposure trends. A marked decrease in air levels of organic solvents was observed during the 1970s LCZ696 mouse and early 1980s, with continuing decrease, thereafter (ExAs Rub 2004). Recently, extensive occupational hygiene measurements have been performed in the

Swedish rubber industry. The surveys were performed mainly in curing areas, and in areas with combined curing and post-processing procedures. High levels

of nitrosamines JNK-IN-8 price in air were detected in certain curing processes (de Vocht et al. 2007a). Also, elevated urinary levels of phthalates (Vermeulen et al. 2005), and 1-hydroxypyrene as an indicator of PAH-exposure were detected at certain work tasks (Balogh et al. 2003). Measurements from other work areas dominated by eFT508 female workers, as post-processing procedures, still are scarce. Also, there are few measurements from the male-dominated mixing areas. Although the substances for which modeling of exposure levels and time trends are available might not be the pertinent ones for reproductive outcome, overall changes

in exposure levels due to better workplace hygiene will indeed be reflected. In this perspective, it is intriguing Org 27569 that we observed a stronger effect on birth-weight, offspring sex ratio, and preterm births during the latter part of the observation period in our study, i.e. after 1987. We have at present no good explanation to this finding. Better exposure estimates, not only for chemical exposures but also for other factors that may affect reproductive outcomes, are indeed needed to elucidate this unexpected finding. From occupational settings outside the rubber industry, there are some indications that paternal solvent exposure is associated with an increased time to pregnancy (Sallmén et al. 1998), and inconsistent findings of low birth weight or preterm birth and spontaneous abortions (Lindbohm 1999). Experimentally, diethylnitrosamine has been shown to be hormonally active (Liao et al. 2001), as well as phthalates (Hoppin et al. 2002). There is evidence from animal data that phthalates have adverse reproductive effects in males (Foeter et al. 2001; Gray et al. 2000; Mylchreest et al. 2002; Nagao et al. 2000), and possibly also females (Ema and Miyawaki 2001). Also, some phthalates have been associated with adverse effects on semen quality in infertile or subfertile couples (Duty et al. 2003; Rozati et al. 2002).