Reaction of arene oxides with nucleosides.

Inosine was reacted with phenanthrene-9,10-oxide and 7,12-dimethylbenz(a)anthracene-5,6-oxide (DMBA-5,6-oxide) to yield the corresponding N-1-alkylinosines. They were shown to undergo hydrolysis to 5-amino-4-imidazole-N-alkylcarboxamide ribosides when heated in the presence of sodium carbonate. Guanosine was reacted with DMBA-5,6-oxide to yield a mixture of N-7-alkylguanines along with a smaller amount of an orcine positive product exhibiting an ultraviolet spectrum resembling that of DMBA-5,6-dihydrodiol.

Tumor-initiating activity of the (+)-(S,S)- and (-)-(R,R)- enantiomers of trans-11,12-dihydroxy-11,12-dihydrodibenzo[a,l]pyrene in mouse skin.

A single administration of enantiomerically pure 11,12-dihydrodiols of dibenzo[a,l]pyrene (DB[a,l]P) on the back of NMRI mice and subsequent chronic treatment with 12-O-tetradecanoylphorbol 13-acetate (TPA) (initiation/promotion assay) revealed strikingly different carcinogenic activities of both enantiomers. Tumor-initiating activity of (-)-(11R,12R)-DB[a,l]P-dihydrodiol, which is the metabolic precursor of the (-)-anti-(11R,12S)-dihydrodiol (13S,14R)-epoxide, was exceptionally higher than the corresponding effect of (+)-(11S,12S)-DB[a,l]P-dihydrodiol, the metabolic precursor of (+)-syn-(11S,12R)-dihydrodiol (13S,14R)-epoxide. After topical application of 10 nmol (-)-11,12-dihydrodiol and promotion with TPA twice weekly for a further 18 weeks 93% of treated animals exhibited four to five tumors. In contrast, no neoplasms were observed after treatment with 10 nmol (+)-11,12-dihydrodiol, whereas in the group exposed to 20 nmol of this enantiomer only 13% of mice developed neoplasms (0.1 tumors/survivor). For DB[a,l]P, considered as the most potent carcinogenic polycyclic aromatic hydrocarbon to date, stereoselective formation of (+)-syn- and (-)-anti-11,12-dihydrodiol 13,14-epoxides via the corresponding enantiomeric 11,12-dihydrodiols has been found to be the principal metabolic activation pathway leading to DNA adducts and mutagenicity. Our study demonstrates that the striking difference in carcinogenic activity in mouse skin of (+)-(11S,12S)- and (-)-(11R,12R)-DB[a,l]P-dihydrodiol convincingly reflects the different genotoxicity, i.e. DNA binding and mutagenicity, of both enantiomers observed earlier.

Polycyclic aromatic hydrocarbons and possible metabolites: convertogenic activity in yeast and tumor initiating activity in mouse skin.

The diploid respiratory-deficient strain of yeast D4-RDII was used to assay PAH and urethane as well as some oxygenated derivatives of PAH and the (aliphatic) epoxide hydrolase inhibitor TCPO for convertogenic (mutagenic) activity. As a positive control, the convertogenic ultimate rat liver carcinogen NOAcAAF was used. PAH and urethane were found inactive as convertogens, TCPO was weakly active, whereas oxygenated electrophilic derivatives of PAH, such as K-region oxides, were found strong convertogens. For comparison, some convertogenic key compounds were assayed for their tumor-initiating activity in mouse skin in the standardized system using TPA as a promotor. PAH were stronger initiators than all oxygenated derivatives of PAH tested. TCPO alone exhibited very weak, if any, initiating activity. It was unable to modify initiation to any significant extent, if administered 5 min prior to administration of an initiator. In the absence of correlation between convertogenic and initiating activity the question of the chemical nature of "ultimate initiators" of mouse skin carcinogenesis awaits further investigation.

Comparative DNA binding of 7,12-dimethylbenz[a]anthracene and some of its metabolites in mouse epidermis in vivo as revealed by the 32P-postlabeling technique.

The binding of some mouse skin metabolites and related derivatives of the tumor initiator 7,12-dimethylbenz[a]anthracene (DMBA) was investigated by 32P-postlabeling analysis after its topical administration. DMBA and trans-3,4-dihydro-3,4-dihydroxy-DMBA (DMBA-3,4-dihydrodiol) both led to the formation of four DNA adducts, which showed a very similar pattern of spots on thin-layer chromatograms. With trans-8,9-dihydro-8,9-dihydroxy-7,12-dimethylbenz[a]anthracene (DMBA-8,9-dihydrodiol) one major adduct was obtained which was chromatographically indistinguishable from one of the DMBA adducts. In contrast, 7-hydroxymethyl-12-methylbenz[a]anthracene (7-OHM-12-MBA) gave rise to two major adducts which were separable from DMBA adducts. 3-hydroxy-7,12-dimethylbenz[a]anthracene (3-OH-DMBA) and 7,12-dimethylbenz[a]anthracene-7,12-epoxide (DMBA-O2) did not lead to detectable amounts of adducts. Quantitative determination of DNA binding showed that an initiating dose (i = 100 nmol) of DMBA yielded approximately 12 adducts/10(7) normal nucleotides. Adduct formation with the same dose of DMBA-3,4-dihydrodiol was 7-8 times higher. At a 4-fold higher dose level, DMBA-8,9-dihydrodiol exhibited a 3- to 6-times weaker binding and 7-OHM-12-MBA a slightly stronger binding than DMBA. Chromatography of the DMBA and DMBA-3,4-dihydrodiol adducts with a solvent containing borate showed a decreased mobility of two out of four adducts in each case. These adducts were also sensitive to oxidation by periodate. The results suggest that two DMBA adducts carried vicinal cis-hydroxyl groups and thus were probably derived from the anti-3,4-dihydrodiol-1,2-oxide(s) of DMBA. The other two adducts were probably derived from the syn-stereoisomer(s). When the DNA-modifying capabilities and initiating activities of the more prominent mouse-skin metabolites are considered in relation to DMBA, DMBA-3,4-dihydrodiol is postulated to be a proximate and DMBA-3,4-dihydrodiol-1,2-oxide(s) to be ultimate initiators.

Comparative tumorigenicity of picene and dibenz[a,h]anthracene in the mouse.

The carcinogenic activity of the two polycyclic aromatic hydrocarbons (PAHs), picene (benzo[a]chrysene) and dibenz[a,h]anthracene (DBA), was determined in NMRI mice by five different experimental protocols in order to find out if picene is a carcinogen as predicted by recent quantum mechanical calculations in contrast to earlier observations which could not confirm any carcinogenic activity of picene. Single s.c. treatment of adult mice with picene or DBA (308 nmol/animal, each) led to the formation of fibrosarcomas in 63.3% of treated animals regardless of the PAH used. Chronic epicutaneous application of both PAHs (total dose 1.36 mumol) to the back of mice resulted in the development of papillomas with a tumor rate of 22% in the case of picene and of 32% in the case of DBA. When newborn mice were s.c. treated once on day 2 of their life with each of the two PAHs (400 nmol/animal), 27.8% of treated animals developed lung adenomas after 40 weeks in the case of picene compared to 92.1% in the case of DBA. Histopathological examination of the tumors in the three experimental models revealed no difference in the type of tumor between picene and DBA. Epicutaneous application of both PAHs (600 nmol/animal) followed by chronic treatment with 12-O-tetradecanoyl-phorbol-13-acetate for 24 weeks led to the formation of papillomas in 93% of animals treated with DBA while picene showed no tumorigenic activity at all. Initiation of tumorigenesis in the two-stage tumor model with 7,12-dimethylbenz[a]anthracene (1 mumol/animal) and chronic treatment with picene (total dose 4.8 mumol) for 24 weeks was equally ineffective in producing tumors in NMRI mice. This rare biological property of picene, which is a complete carcinogen, yet at most a very weak tumor initiator, is explained in terms of its inefficient biotransformation to mutagenic and carcinogenic metabolites as compared to the strong tumor initiator DBA.