Formation of DNA adducts in mouse skin treated with metabolites of chrysene

Biological effects of polycyclic aromatic hydrocarbons (PAH) and their first metabolic products in in vivo exposed Atlantic cod (Gadus morhua)

The monitoring of the presence of polycyclic aromatic hydrocarbons (PAH) in the aquatic environment is a worldwide activity since some of these compounds are well-established carcinogens and mutagens. Contaminants in this class are in fact regarded as priority hazardous substances for environmental pollution (Water Framework Directive 2000/60/EC). In this study, Atlantic cod (Gadus morhua) was selected to assess in vivo effects of two PAH and their first metabolic products, namely, the corresponding trans-dihydrodiols, using biological markers. Fish were exposed for 1 wk to a single PAH (naphthalene or chrysene) and its synthetic metabolites ((1R,2R)-1,2-dihydronaphthalene-1,2-diol and (1R,2R)-1,2-dihydrochrysene-1,2-diol) by intraperitoneal injection in a continuous seawater flow system. After exposure, PAH metabolism including PAH metabolites in bile and ethoxyresorufin O-deethylase (EROD) activity, oxidative stress glutathione S-transferases (GST) and catalase (CAT) activities, and genotoxicity such as DNA adducts were evaluated, as well as general health conditions including condition index (CI), hepatosomatic index (HSI), and gonadosomatic index (GSI). PAH metabolite values were low and not significantly different when measured with the fixed-wavelength fluorescence screening method, while the gas chromatography-mass spectroscopy (GC-MS) method showed an apparent dose response in fish exposed to naphthalene. DNA adduct levels ≥0.16 × 10(-8) relative adduct level (RAL) were detected. It should be noted that 0.16 × 10(-8) RAL is considered the maximal acceptable background level for this species. The other biomarkers activities of catalase, GST, and EROD did not display a particular compound- or dose-related response. The GSI values were significantly lower in some chrysene- and in both naphthalene- and naphthalene diol-exposed groups compared to control.

Differences between blood and liver aromatic DNA adduct formation

Aromatic DNA adducts in the livers and blood of grey mullet (Mugil sp.) have been monitored between 1993 and 1996 by the isolation of DNA and the postlabeling of the DNA adducts with 32P. The grey mullet were sampled from three well-characterised harbours, two in the northeastern Mediterranean and one in the northeastern Black Sea near Trabzon close to a site of aquaculture. One of the northeastern Mediterranean harbours was highly polluted with polynuclear aromatic hydrocarbons (PAHs) and was rich in inorganic nutrients. Larger grey mullet lived in this harbour than the other harbours and their livers possessed approximately 100 aromatic DNA adducts per 10(8) nucleotides. The livers from grey mullet in the other two harbours possessed < or = 25 aromatic DNA adducts per 10(8) nucleotides but these concentrations depended on a variety of factors. Blood cell being regenerated more rapidly than liver cells, it is found that generally the ratio of DNA adduct concentrations in piscine liver and blood will increase with the pollution of the surrounding marine environment. Fishes are acceptable models for the metabolism of xenobiotics and the associated formation of harmful aromatic DNA adducts in organisms.

DNA adducts produced by oils, oil fractions and polycyclic aromatic hydrocarbons in relation to repair processes and skin carcinogenesis

Ten polycyclic aromatic hydrocarbons (PAHs) mainly with three or four aromatic rings were tested for their ability to induce DNA adduct formation in mouse skin. Four of these were selected to investigate adduct formation and loss over a period of 8 days. Three mineral oils were also examined for their adduct forming ability and one was selected for adduct formation and loss over a period of 8 days. In addition, fractions derived from the same oil containing 2-3- and 4-6-ring aromatic compounds were applied to mouse skin in a non-carcinogenic oil vehicle and adduct levels were observed over an 8-day period. It was found that PAHs that had no mutagenic, initiating or carcinogenic activity and those that had mutagenic activity in bacteria but no initiating activity in mouse skin failed to produce DNA adducts in mouse skin. Two of the three PAHs with initiating activity and both complete carcinogens produced clear evidence of adduct formation, the adduct levels produced by complete carcinogens being 100-1000 times greater than those produced by initiators. Examination of adduct formation and loss with the carcinogenic PAHs benzo[a]pyrene and 5-methylchrysene over an 8-day period showed a peak at 24 h and an apparent two-phase process of adduct loss. It is suggested that the first steep loss was due to DNA repair and that the more gradual subsequent loss was probably due to epidermal hyperplasia and desquamation. With the initiator 1, 4-dimethylphenanthrene (three rings) a peak of adduct formation was seen at 2 days and adduct levels were not reduced much by 8 days. This suggested that, with initiators, adduct formation and repair may be spread over a longer period than with complete carcinogens. With the whole oils, clear evidence of adduct formation was seen with both a carcinogenic non-solvent-refined oil and with a non-carcinogenic residual oil. The level of adduct formation with the residual oil, however, was much lower than with the carcinogenic oil. When adduct formation by the carcinogenic oil was examined over 8 days, the pattern of adduct formation and loss was similar to that of a tumour initiator rather than a complete carcinogen. Peak adduct levels on the diagonal of the thin-layer chromatography (TLC) plates seemed to occur at 1 and 4 days after treatment, with no clear reduction after 8 days. From examination of adducts formed by the 2-3-ring and 4-6-ring aromatic fractions, it appeared that the main adduct spots produced by the carcinogenic oil were due to the 2-3-ring aromatic components of the oil. Adduct spots near the vertical axis of the TLC plates were also seen with the 2-3-ring and 4-6-ring fractions. The relevance of these spots is uncertain, but if they truly represent adducts, the findings suggest that they are due mainly to 4-ring PAHs. The studies suggest that the activity of carcinogenic oils is largely due to substituted 3- and 4-ring polycyclic aromatic compounds and that more attention should be paid to substituted 3-ring compounds in predicting the carcinogenic potential of oils from analytical data.

Improved reversed-phase high-performance liquid chromatographic separation of 32P-labelled nucleoside 3',5'-bisphosphate adducts of polycyclic aromatic hydrocarbons

32P-Postlabelling is a sensitive technique for the detection and analysis of carcinogen-DNA adducts. In this paper we describe the development of an improved high-performance liquid chromatography (HPLC) method for the separation of 32P-labelled 3',5'-bisphosphates of nucleosides modified by reactive derivatives of carcinogenic polycyclic aromatic hydrocarbons (PAH). Optimal resolution of the major 32P-postlabelled DNA adducts formed by the anti-diol-epoxides of ten PAH was achieved using a phenyl-modified silica gel column with a gradient of methanol in phosphate buffer at low pH and high ionic strength. Use of a radioactivity flow detector coupled to the HPLC apparatus allowed detection of subfemtomole quantities of labelled adducts.

Formation of DNA adducts in the skin of psoriasis patients, in human skin in organ culture, and in mouse skin and lung following topical application of coal-tar and juniper tar

Preparations of coal-tar and juniper tar (cade oil) that are used in the treatment of psoriasis are known to contain numerous potentially carcinogenic polycyclic aromatic hydrocarbons (PAH). Evidence of covalent binding to DNA by components of these mixtures was sought in a) human skin biopsy samples from 12 psoriasis patients receiving therapy with these agents, b) human skin explants maintained in organ culture and treated topically with the tars, and c) the skin and lungs of mice treated with repeated doses of the formulations following the regimen used in the clinic. DNA was isolated from the human and mouse tissues and digested enzymically to mononucleotides. 32P-Post-labeling analysis revealed the presence of aromatic DNA adducts in the biopsy samples at levels of up to 0.4 fmol total adducts/microgram DNA. Treatment of human skin in organ culture produced similar levels of adducts, while treatment with dithranol, a non-mutagenic therapeutic agent, resulted in chromatograms indistinguishable from those from untreated controls. In mouse skin, coal-tar ointment and juniper tar gave similar DNA adduct levels, with a similar time-course of removal: maximum levels (0.5 fmol/microgram DNA) at 24 h after the final treatment declined rapidly to 0.05 fmol/microgram at 7 d, thereafter declining slowly over the succeeding 25 d. However, while coal-tar ointment produced only very low levels of adducts in mouse lung (less than 0.03 fmol/microgram DNA), juniper tar produced adducts at a high level (0.7 fmol/microgram DNA) that were persistent in this tissue. These results provide direct evidence for the formation of potentially carcinogenic DNA damage in human and mouse tissue by components of these therapeutic tar preparations.

Formation and persistence of benzo[a]pyrene-diolepoxide-DNA adducts in liver of English sole (Parophrys vetulus)

The formation of DNA adducts from the carcinogenic environmental pollutant benzo[a]pyrene (BaP) was investigated in liver of English sole (Parophrys vetulus), a fish species that exhibits a high prevalence of liver neoplasms in several polycyclic aromatic hydrocarbon (PAH)-contaminated areas of Puget Sound, WA. Analysis by the 32P-postlabeling assay of hepatic DNA digests from English sole exposed parenterally to BaP showed the presence of BaP-diol epoxide (BaPDE)-DNA adducts. When English sole were injected with 2-15 mg BaP/kg body wt., one major adduct was detected and was identified as the anti-BaPDE-DNA adduct. Moreover, in English sole sampled at 1, 28 and 60 days post-exposure to 15 mg BaP/kg body wt., there was no significant change in the level of the anti-BaPDE-DNA adduct. The autoradiographs of 32P-labeled hepatic DNA digests from fish exposed to 100 mg BaP/kg body wt. showed an elongated spot suggesting the presence of more than one adduct. Chromatography on large polyethyleneimine sheets (20 x 20 cm) showed 2 spots with the same chromatographic characteristics as those of syn- and anti-BaPDE-deoxyguanosine adduct standards. Mild acid hydrolysis of hepatic DNA of English sole, exposed to 100 mg BaP/kg body wt., also revealed the presence of tetrols derived from both anti- and syn-BaPDE, thus confirming the presence of syn- and anti-BaPDE. In fish exposed to 2-100 mg BaP/kg body wt., a linear (0.996) dose response for anti-BaPDE-DNA adduct formation was observed. The results from this study offer the first direct evidence for the formation of the suspected ultimate carcinogen, BaPDE, in liver of English sole exposed to BaP in vivo and thus further support the hypothesis that exposure to PAHs is an important factor in the etiology of hepatic neoplasms in English sole from contaminated sites.

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.