In a plastic boat company we studied workers' attitudes toward wearing respiratory protective equipment and differences in styrene exposure received with and without respirators. The workers studied used either half-facepiece air-purifying or full-face air-supplied respirators as much as possible during the first day of the study. On the second day respirators were used only for short periods or-not at all. Individual styrene exposures were measured by personal air sampling in the breathing zone. When using respirators the exposure was measured both inside and outside the respirators. The styrene metabolites mandelic and phenylglyoxylic acids were determined in urine samples collected during the workday. The eleven workers studied used the respirators 52% of the time on the first day and 7% of the time on the second. The reasons for not wearing respirators were that they delayed work, were too tight and uncomfortable, made it difficult to breath, and/or became too warm. The use of respirators during work operations such as spraying, laminating, and painting reduced the styrene exposure by 56%-92%. The excretion rate of mandelic and phenylglyoxylic acids in urine collected at the end of the working day was 30%-99% lower when respirators were worn than when they were not.

Polychlorinated dioxins (PCDD) and dibenzofurans (PCDF) have been identified in technical products and pesticides, most of which are not very widely used today. Other sources are incinerators of various types like MSW incinerators, hazardous waste incinerators and industrial incinerators. PCDDs and PCDFs have also been identified in exhausts from cars running on leaded gasoline with halogenated additives. Background levels of PCDDs and PCDFs have been identified in fish and other aquatic organisms from the Great Lakes and the Baltic Sea, and also in human adipose tissue samples from U.S.A., Canada, Sweden, Japan and Vietnam as well as in samples of breast milk from Sweden, Denmark, West Germany, the Netherlands, Yugoslavia and Vietnam. The isomeric pattern in all these biological samples is very similar. The relative importance of different sources to the general background is difficult to estimate although the contribution of direct inhalation from point sources like MSW incinerators is small.

Polychlorinated dioxins and dibenzofurans have been identified in technical products and pesticides, most of which are not very widely used today. Other sources are incinerators of various types like MSW incinerators, but also hazardous waste incinerators and industrial incinerators. PCDDs and PCDFs have also been identified in exhausts from cars running on leaded gasoline with halogenated additives. Background levels of PCDDs and PCDFs have been identified in fish and other aquatic organisms from the Great Lakes and the Baltic Sea, and also in human adipose tissue samples from USA, Canada, Sweden, Japan and Viet Nam as well as in samples of breast milk from Sweden, Denmark, West Germany, the Netherlands, Yugoslavia and Viet Nam. The isomeric pattern in all these biological samples is very similar.