Metabolism of benzo[a]pyrene and persistence of DNA adducts in the brown bullhead (Ictalurus nebulosus).

1. The in vitro metabolism of [3H]benzo[a]pyrene (BP) and [14C]benzo[a]pyrene-7,8-dihydrodiol (BP-7,8-diol) by liver of brown bullhead (Ictalurus nebulosus) was characterized, as was the formation and persistence of BP-DNA adducts in vivo. 2. Compared to rat liver microsomes, bullhead liver microsomes produced relatively larger amounts of BP-7,8-diol (predominantly the [-] enantiomer) and smaller amounts of of BP-7,8-diol (predominantly the [-] enantiomer) and smaller amounts of BP-4,5-diol. 3. BP phase I metabolites were efficiently converted by freshly isolated bullhead hepatocytes to conjugates, predominantly glucuronides. 4. BP-7,8-diol was metabolized by hepatocytes 4-fold more rapidly than was BP and was converted to approximately equal amounts of glucuronides, glutathione conjugates and sulfates. 5. BP-DNA adducts formed in bullhead liver with a lag time of several days and maximum adduct formation at 25-30 days. The major adduct was anti-BPDE-deoxyguanosine.

Formation and persistence of DNA adducts in the liver of brown bullheads exposed to benzo[a]pyrene.

The formation and persistence of benzo[a]pyrene (BP)-DNA adducts in the liver of brown bullheads (Ictalurus nebulosus) treated with the hydrocarbon (20 mg/kg body wt, i.p.) was investigated using the 32P-postlabeling assay. The highest level of covalent binding of BP to liver DNA (188 fmol BP adducts/mg DNA) was observed 25-30 days following treatment. After 70 days, the adduct level in liver DNA had declined to approximately 26% of the maximum adduct level. One major BP-DNA adduct and several minor ones were detected in the liver. The major adduct co-chromatographed with anti-BP-7,8-diol-9,10-epoxide-deoxyguanosine (anti-BPDE-dGuo) adduct. The data suggest that brown bullheads metabolically activate BP by the same mechanism as the mammalian systems susceptible to carcinogenic effects of the hydrocarbon.

Comparative metabolism of benzo[f]quinoline by liver microsomes from brown bullheads and rats.

1. Liver microsomes from rats were considerably more active in metabolizing benzo[f]quinoline (B f Q) than those from brown bullheads (Ictalurus nebulosus). 2. The main B f Q metabolites formed by both rat and brown bullhead liver microsomes were qualitatively similar and included B f Q-7,8-dihydrodiol, B f Q-9,10-dihydrodiol, B f Q-N-oxide, 7-hydroxy B f Q, and 9-hydroxy B f Q. 3. The liver microsomes from control brown bullheads and rats metabolized B f Q primarily at the 7,8-and 9,10-positions, respectively, whereas in the case of microsomes from 3-methylcholanthrene (3-MC)-treated rats or brown bullheads, the major site of metabolic attack was the 7,8-position. 4. A 3-MC-type of cytochrome P-450 appears to be primarily responsible for the oxidation of B f Q by control brown bullhead liver microsomes, whereas a phenobarbital-inducible type of cytochrome P-450 seems to be involved in the metabolism of B f Q by control rat liver microsomes.

Hepatic DNA adduct formation in rats treated with benzo[f]quinoline.

The formation of hepatic DNA adducts in male Sprague-Dawley rats following i.p. administration of benzo[f]quinoline (BfQ) was examined using a 32P-post-labeling assay. BfQ exhibited a low binding (11-27 amol adducts/microgram DNA) to liver DNA. Two BfQ-nucleoside adducts (one major and one minor) were detected. The BfQ-DNA adducts formed in vivo were chromatographically distinct from the adducts formed by the reaction of calf thymus DNA in vitro with BfQ-5,6-oxide, syn-7 beta,8 alpha-dihydroxy-9 beta,10 beta-epoxy-7,8,9,10-tetrahydroBfQ, anti-9 alpha,10 beta-dihydroxy-7 alpha,8 alpha-epoxy-7,8,9,10-tetrahydroBfQ, or anti-7 beta,8 alpha-dihydroxy-9 alpha,10 alpha-epoxy-7,8,9,10-tetrahydroBfQ-N- oxide. These results suggest that the bay-region diol epoxide of BfQ, unlike the bay-region diol epoxide derivatives of polynuclear aromatic hydrocarbons, is not involved in the covalent binding of BfQ to DNA.

Comparative metabolism of phenanthrene and benzo[f]quinoline by rat liver microsomes.

The metabolism of benzo[f]quinoline (BfQ) and its carbon analog phenanthrene has been compared in incubations with liver microsomes from control, 3-methylcholanthrene (3-MC)- and phenobarbital (PB)-pretreated rats. The rates of phenanthrene metabolism by the three types of microsomes were 0.7, 4.1 and 1.5 nmol/mg protein per min, respectively; the values for BfQ were 0.5, 3.7 and 2.5, respectively. Besides N-oxidation, the metabolism of BfQ by all the above microsomes was almost exclusively at the benzo-ring (49-69%) while that of phenanthrene was predominantly at the K-region (50-71%). Phenanthrene-1,2-dihydrodiol, a precursor of the bay-region diol epoxide of phenanthrene, was produced many times more than phenanthrene-3,4-dihydrodiol by both 3-MC- and PB-induced microsomes. While BfQ-7,8-dihydrodiol, the precursor of the bay-region diol epoxide of BfQ, was the predominant metabolite with 3-MC-induced microsomes, it was a minor metabolite with PB-induced microsomes. The benzo-ring oxidation of BfQ, but not of phenanthrene, was position-specific, i.e. predominantly 7,8-oxidation by 3-MC-induced microsomes and 9,10-oxidation by PB-induced microsomes, and implies that aza-substitution results in a site-specific attack by different cytochromes P-450.