Comparative studies of the metabolic activation of chrysene in rodent and human skin

ATSDR evaluation of health effects of chemicals. IV. Polycyclic aromatic hydrocarbons (PAHs): understanding a complex problem

Polycyclic Aromatic Hydrocarbons (PAHs) are a group of chemicals that are formed during the incomplete burning of coal, oil, gas, wood, garbage, or other organic substances, such as tobacco and charbroiled meat. There are more than 100 PAHs. PAHs generally occur as complex mixtures (for example, as part of products such as soot), not as single compounds. PAHs are found throughout the environment in the air, water, and soil. As part of its mandate, the Agency for Toxic Substances and Disease Registry (ATSDR) prepares toxicological profiles on hazardous chemicals, including PAHs (ATSDR, 1995), found at facilities on the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) National Priorities List (NPL) and which pose the most significant potential threat to human health, as determined by ATSDR and the Environmental Protection Agency (EPA). These profiles include information on health effects of chemicals from different routes and durations of exposure, their potential for exposure, regulations and advisories, and the adequacy of the existing database. Assessing the health effects of PAHs is a major challenge because environmental exposures to these chemicals are usually to complex mixtures of PAHs with other chemicals. The biological consequences of human exposure to mixtures of PAHs depend on the toxicity, carcinogenic and noncarcinogenic, of the individual components of the mixture, the types of interactions among them, and confounding factors that are not thoroughly understood. Also identified are components of exposure and health effects research needed on PAHs that will allow estimation of realistic human health risks posed by exposures to PAHs. The exposure assessment component of research should focus on (1) development of reliable analytical methods for the determination of bioavailable PAHs following ingestion, (2) estimation of bioavailable PAHs from environmental media, particularly the determination of particle-bound PAHs, (3) data on ambient levels of PAHs metabolites in tissues/fluids of control populations, and (4) the need for a critical evaluation of current levels of PAHs found in environmental media including data from hazardous waste sites. The health effects component should focus on obtaining information on (1) the health effects of mixtures of PAHs particularly their noncarcinogenic effects in humans, and (2) their toxicokinetics. This report provides excerpts from the toxicological profile of PAHs (ATSDR, 1995) that contains more detailed information.

HPLC separation of 32P-postlabelled benzo[b]fluoranthene-DNA adducts

Analysis using 32P-postlabelling and a recently developed HPLC method resolved the adduct formed by reaction of the benzo[b]fluoranthene (BbF) anti-bay-region diol-epoxide with DNA from the more polar major adduct produced by the hydrocarbon in three different biological systems. In each case, the adduct formed from the anti-bay-region diol-epoxide constituted only a minor proportion of the total DNA modification. Comparisons of the DNA adducts formed from the hydrocarbon with those formed in microsomal incubations from the putative metabolites BbF-9,10-diol, anti-BbF-9,10-diol-11,12-oxide and the 5,9,10- and 6,9,10-BbF-triols indicate that the predominant pathway for BbF activation in skin probably involves a bay-region triol-epoxide possessing a phenolic OH-group on the peninsula ring.

DNA adducts in human and mouse skin maintained in short-term culture and treated with petrol and diesel engine lubricating oils

Human and mouse skin samples maintained in short-term organ culture were treated topically with used engine oils from petrol- and diesel-powered vehicles. Mice were also treated topically in vivo for comparison. DNA was isolated and analysed by 32P-postlabelling and the labeled DNA digests were resolved on polyethyleneimine-cellulose tlc sheets. A large number of radioactive adduct spots were observed in DNA from skin treated with the used petrol-engine oil, indicating the formation of adducts by many components of the complex oil mixture. Total adduct levels were similar in mouse skin (both in vivo and in vitro) and in human skin, although qualitative differences in the adduct maps were apparent between the human and mouse skin DNA. Treatment with the used diesel engine oil produced adduct levels no greater than that of control samples in mouse skin (in vivo and in vitro), although significant levels were found in human skin DNA from one donor. The results correlate well with the carcinogenic activity of these oils in experimental animals, helping to substantiate the conclusion that petrol engine oils (but not diesel engine oils) may present a carcinogenic risk to man if appropriate measures to minimise skin contact are not observed.

Formation of DNA adducts in human skin maintained in short-term organ culture and treated with coal-tar, creosote or bitumen

Adult and foetal human skin samples maintained in short-term organ culture were treated topically with solutions of coal-tar, creosote or bitumen, then DNA was isolated and analysed by 32P-post-labelling for the presence of aromatic DNA adducts. Autoradiographs of the 32P-labelled adducts resolved on polyethyleneimine-cellulose tlc sheets revealed a band of radioactivity indicative of the formation of adducts by a large number of components in these complex carcinogenic mixtures. Single doses of the materials, similar to those used to initiate tumours in experimental animals, resulted in the formation of approximately 0.3 fmol total adducts/micrograms DNA. The levels of adducts formed in human skin are thus similar to those formed in mouse skin after administration of doses known to be carcinogenic to the latter. The results provide direct evidence of DNA damage in human skin by materials strongly suspected of being carcinogenic to humans, and point to a method for evaluating other complex mixtures of aromatic chemicals for their potential carcinogenic hazard.

Stereoselective aspects of the metabolic activation of benzo[a]pyrene by human skin in vitro

Benzo[a]pyrene (BP) is activated within tissues in both a regio- and a stereoselective manner and, since human skin is sensitive to tumour induction by polycyclic aromatic hydrocarbons (PAH), the steroselective metabolism of BP in this tissue has been investigated. Samples of skin from eleven individuals were treated with [3H]BP in short-term organ culture. Two samples were also treated with mixtures of [14C](+)- and (-)-trans-7,8-dihydro-7,8-dihydroxybenzo[a]pyrene (BP-7,8-dihydrodiol) in varying proportions. Following application of [3H] BP, more 7,8-dihydrodiol was recovered from the skin itself than from the culture fluid in ten cases; no 7.8-dihydrodiol was detected in extracts from the eleventh. The 7,8-dihydrodiol metabolite was extracted predominantly (range 74-greater than 99%) as the (-)-enantiomer in nine of these ten patients, although proportionately more (+)-enantiomer was recovered from the culture fluid than from the skin in each case. The relative proportions of [3H]BP tetrols derived from syn- and anti-7,8-dihydroxy-9,10-oxy-7,8,9,10-tetrahydroxybenzo[a]pyrene (BPDE) detected in these extracts was more variable. When skin samples were treated with [14C]BP-7,8-dihydrodiol, more anti- than syn-BPDE-derived tetrols were extracted, irrespective of the optical purity of the dihydrodiol applied. These findings provide evidence for interindividual variations in the stereoselective metabolism of BP, which may be of some importance in determining individual susceptibility to PAH-induced skin carcinogenesis.

Effects of inducers on the regio- and stereoselective metabolism of benzo[a]pyrene by mouse tissue microsomes

The metabolism of benzo[a]pyrene (BP) by microsomal fractions of the skin, lungs and liver of the mouse, and the effects on this process of pretreatment with the xenobiotics phenobarbital (PB) and 3-methylcholanthrene (3-MC) were examined. Differences between the untreated tissues were found both in terms of the total amounts of diol recovered and in the relative proportions of the individual diols extracted following incubation. Induction with PB or 3-MC significantly altered the profiles of metabolic diols obtained with epidermal and hepatic microsomes compared with their respective controls. Pulmonary microsomes showed similar trends to those obtained with liver microsomes but these were not statistically significant. The optical purity of the BP-7,8-diol that was formed by each microsomal type was examined by direct resolution of the enantiomers on HPLC using a chiral stationary phase. In each case the (-)-7R,8R-enantiomer predominated. Pretreatment with 3-MC significantly decreased the optical purity of BP-7,8-diol recovered from incubations with skin microsomes, but significantly increased the optical purity of the diol extracted from incubations with lung and liver microsomes. In addition to the diols, an unidentified BP metabolite was found that eluted between BP-9,10- and 4,5-diol on a reverse-phase high-performance liquid chromatography (HPLC) system and which represented a major product in extracts of incubations of BP with both induced and uninduced skin and lung microsomal fractions.