Abstract
In vivo studies with laboratory animals as well as in vitro studies with bacteria and mammalian cell cultures have demonstrated that the mutagenic and/or carcinogenic properties of numerous PAHs require metabolic transformation. Metabolism of PAHs has been explored in vitro using cellular microsomal fractions, mammalian cell cultures and later genetically engineered cells expressing cytochromes P450 from several species including humans. Balancing the carcinogenic potential of some environmental matrices (vehicle exhaust, condensate of hard coal combustion effluents, cigarette smoke condensate, used motor oil) after separation into sub-fractions evidenced that the carcinogenic effect may be attributed almost exclusively to PAH. Mixtures of well-known carcinogenic PAH in concentrations as present in these matrices, however, did not explain the total biological effect. Thus, it had been speculated that either very potent unknown carcinogens are still hidden in the PAH fraction, or that synergistic effects (enzyme induction) play a significant role. In parallel to these carcinogenicity studies, the metabolism of various PAHs has been investigated in rat liver microsomes from untreated animals as well as from animals pre-treated with inducers of cytochrome P450. It was found that even non-carcinogenic PAHs possess a significant inducing potential. Moreover, in several mammals a highly species-specific metabolism of PAH could be observed allowing a critical view to the extrapolation from animal experiments to the human situation. This was further confirmed by experiments with mammalian cell cultures including human ones as well as by metabolic studies with genetically engineered Chinese hamster V79 cells singularly expressing various cytochrome P450 enzymes from a number of different species (human, rat, mouse, fish). With these cell lines metabolic studies were carried out with a larger number of PAHs as substrates including phenanthrene, pyrene, chrysene, benzo[a]anthracene, benzo[c]phenanthrene, benzo[a]pyrene, dibenzo[a,l]pyrene, and benzo[c]chrysene. Based on the metabolism results, analytical methods have been developed to determine urinary biomarkers of human PAH exposure. Human biomonitoring studies have been performed with different occupationally exposed individuals as well as within smokers and non-smokers of the general population. Endogenous PAH exposure levels and changes in the urinary excreted metabolic profile depending on exposure level have been determined.
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