Unusual patterns of benzo[a]pyrene metabolites and DNA-benzo[a]pyrene adducts produced by human placental microsomes in vitro

Human placental microsomes were incubated with [³H]benzo[a]pyrene (BP) and Salmon sperm DNA and the resulting metabolite-nucleoside complexes resolved by Sephadex LH-20 chromatography. The metabolite pattern was analyzed by high-pressure liquid chromatography (HPLC). The incubates were also co-chromatographed with extracts obtained from incubates with rat liver microsomes and [¹⁴C]BP. Phenols, quinones and 7,8-dihydrodiol were detected in the placental incubates. Both 9,10- and 4,5-dihydrodiols were very low as compared with control rat liver samples. Placental microsomes catalyzed the binding of BP metabolites to DNA in vitro, giving rise to two main complexes which co-chromatographed with rat liver-produced peaks attributable to 7,8-diol-9,10-epoxide and 7,8-oxide and/or quinones when metabolized further. The nucleoside metabolite peaks attributable to 4,5-oxide and 9-phenol-4,5-oxide were lacking when compared with the binding pattern catalyzed by rat liver. Both the total binding and specific metabolite-nucleoside adducts in the placenta correlated with fluorometrically measured aryl hydrocarbon hydroxylase (AHH) activity and with the amount of dihydrodiol formed. The results demonstrate that both the metabolite pattern and the nucleoside-metabolite complexes formed by the placental microsomes in vitro differed greatly from those produced by rat liver microsomes. These studies also suggest that it is not possible to predict specific patterns of DNA binding from AHH measurements or even from BP metabolite patterns, especially when comparing different tissues and species.     

Some properties of vicinal diol-epoxides derived from benzo(a)anthracene and benzo(a)pyrene

The alkylating properties of pairs of syn- and anti-isomers of 2 diol-epoxides derived from benzo(a)pyrene (BP) and of 1 derived from benz(a)anthracene (BA) have been investigated. Of the anti-diol-epoxides, anti-BP 7,8-diol-9,10-oxide was the most reactive compound towards DNA, towards sodium p-nitrothiophenolate in a non-aqueous solvent system, and towards 4-(p-nitrobenzyl)pyridine in aqueous solution; anti-BP 9,10,-diol-7,8-oxide was of intermediate reactivity and anti-BA 8,9-diol-10,11-oxide was least reactive. The syn-diol-epoxides gave unsatisfactory results with DNA and 4-(p-nitrobenzyl)pyridine because of their rapid solvolysis in aqueous solution, but with sodium p-nitrothiophenolate showed the order of reactivity syn-BP 7,8-diol-9,10-oxide greater than syn-BA 8,9-diol-10,11-oxide greater than syn-BP 9,10-diol-7,8-oxide. The products of the reaction between diol-epoxides and nucleic acids were examined by Sephadex LH-20 chromatography followed by high-pressure liquid chromatography (HPLC) and the diol-epoxides were shown to react principally with the guanosine and adenosine moieties of RNA.     

High mutagenicity and toxicity of a diol epoxide derived from benzo[a]pyrene

(±)-7β,8α-Dihydroxy-9β,10β-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (BP 7,8-diol-9,10-epoxide) is a suspected metabolite of benzo[a]pyrene that is highly mutagenic and toxic in several strains of $\text{Salmonella}\text{typhimurium}$ and in cultured Chinese hamster V79 cells. BP 7,8-diol-9,10-epoxide was approximately 5, 10 and 40 times more mutagenic than benzo[a]pyrene 4,5-oxide (BP 4,5-oxide) in strains TA 98 and TA 100 of $\text{S.}\text{typhimurium}$ and in V79 cells, respectively. Both compounds were equally mutagenic to strain TA 1538 and non-mutagenic to strain TA 1535 of $\text{S.}\text{typhimurium}$. The diol epoxide was toxic to the four bacterial strains at 0.5–2.0 nmole/plate, whereas BP 4,5-oxide was nontoxic at these concentrations. In V79 cells, the diol epoxide was about 60-fold more cytotoxic than BP 4,5-oxide.     

Binding of metabolically activated benzo(a)pyrene to DNA and histones of rat liver,lung and regenerating liver

Binding of metabolically activated benzo(a)pyrene (BP) to the DNA and histones of nuclei isolated from rat liver, lung, and regenerating liver was examined. Separation of enzymically degraded DNA by Sephadex LH-20 chromatography resulted in several peaks of radioactivity and the major peak was probably derived from the binding of 7,8-diol-9,10-epoxide of BP with DNA. A high level of BP metabolites was also bound to the Hl histone fraction. The patterns of BP binding with the components of nuclei from the different cell types were similar. Implications of these observations as related to carcinogenic tissue susceptibility are discussed.     

Metabolism and covalent binding of benzo[alpha]pyrene in human peripheral lung

Short-term organ cultures of peripheral lung from lung cancer patients metabolise benzo[alpha]pyrene to ethylacetate-soluble metabolites, which covalently bind to tissue macromolecules. The nature and quantities of metabolites formed and the extent of covalent binding are dependent upon the time of incubation, the substrate concentration and interindividual variability in the metabolic activity of the lung. Individuals whose lungs rapidly metabolise the carcinogen exhibit more extensive further metabolism of primary metabolites and higher levels of covalent binding. Certain striking differences in the relative retention in the tissue or release into the extra-cellular medium of different metabolites have been found as illustrated by the observation that the ratio of 7,8-dihydro-7,8-dihydroxybenzo[alpha]-pyrene to 9,10-dihydro-9,10-dihydroxybenzo[alpha]pyrene was always significantly higher in the tissue than in the extracellular medium.     

Ethoxyquin feeding to rats increases liver microsome-catalyzed formation of benzo(a)pyrene diol epoxide — DNA adduct

The ability of rat liver microsomes to catalyze the formation of benzo(a)pyrene 7,8-diol-9,10-epoxide — DNA nucleoside adduct was increased threefold by feeding 0.5% ethoxyquin to the animals. Microsomal epoxide hydratase activity was enhanced i parallel by a factor of 3 while aryl hydrocarbon hydroxylase activity was not induced. Liver microsomes from rat pretreated with 3-methylcholanthrene produced an increased proportion of diol epoxide — DNA adduct when ethoxyquin had been fed to the animals. The main chromatographic peak formed by microsomes from 3-methylcholanthrene treated rats which contains DNA adducts of secondary benzo(a)pyrene phenol metabolites is reduced when the animals had received ethoxyquin.     

Effects of a 6-fluoro substituent on the metabolism of benzo(a)pyrene 7,8-dihydrodiol to bay-region diol epoxides by rat liver enzymes

Metabolism of trans-7,8-dihydroxy-7,8-dihydro-6-fluorobenzo(a)pyrene by liver microsomes from 3-methylcholanthrene-treated rats and by a highly purified monooxygenase system, reconstituted with cytochrome P-450c, has been examined. Although both the fluorinated and unfluorinated 7,8-dihydrodiol formed from benzo(a)pyrene by liver microsomes share (R,R)-absolute configuration, the fluorinated dihydrodiol prefers the conformation in which the hydroxyl groups are pseudodiaxial due to the proximate fluorine. The fluorinated 4,5- and 9,10-dihydrodiols are also greater than 97% the (R,R)-enantiomers. For benzo(a)pyrene, metabolism of the (7R,8R)-dihydrodiol to a bay-region 7,8-diol-9,10-epoxide in which the benzylic hydroxyl group and epoxide oxygen are trans constitutes the only known pathway to an ultimate carcinogen. With the microsomal and the purified monooxygenase system, this pathway accounts for 76-82% of the total metabolites from the 7,8-dihydrodiol. In contrast, only 32-49% of the corresponding diol epoxide is obtained from the fluorinated dihydrodiol and this fluorinated diol epoxide has altered conformation in that its hydroxyl groups prefer to be pseudodiaxial. Much smaller amounts of the diastereomeric 7,8-diol-9,10-epoxides in which the benzylic hydroxyl groups and the epoxide oxygen are cis are formed from both dihydrodiols. As the fluorinated diol epoxides are weaker mutagens toward bacteria and mammalian cells relative to the unfluorinated diol epoxides, conformation appears to be an important determinant in modulating the biological activity of diol epoxides. One of the more interesting metabolites of 6-fluorinated 7,8-dihydrodiol was a relatively stable arene oxide, probably the 4,5-oxide, which is resistant to the action of epoxide hydrolase.     

Metabolism of benzo[a]pyrene VI. Stereoselective metabolism of benzo[a]pyrene and benzo[a]pyrene 7,8-dihydrodiol to diol epoxides

(±)-7β,8α-Dihydroxy-9β,10β-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (diol epoxide-1) and (±)-7β,8α-dihydroxy-9α,10α-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (diol epoxide-2) are highly mutagenic diol epoxide diastereomers that are formed during metabolism of the carcinogen (±)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene. Remarkable stereoselectivity has been observed on metabolism of the optically pure (+)- and (?)-enantiomers of the dihydrodiol which are obtained by separation of the diastereomeric diesters with (?)-α-methoxy-α-trifluoromethylphenylacetic acid. The high stereoselectivity in the formation of diol epoxide-1 relative to diol epoxide-2 was observed with liver microsomes from 3-methylcholanthrene-treated rats and with a purified cytochrome P-448-containing monoxygenase system where the (?)-enantiomer produced a diol epoxide-2 to diol epoxide-1 ratio of 6 : 1 and the (+)-enantiomer produced a ratio of 1 : 22. Microsomes from control and phenobarbital-treated rats were less stereospecific in the metabolism of enantiomers of BP 7,8-dihydrodiol. The ratio of diol epoxide-2 to diol epoxide-1 formed from the (?)- and (+)-enantiomers with microsomes from control rats was 2 : 1 and 1 : 6, respectively. Both enantiomers of BP 7,8-dihydrodiol were also metabolized to a phenolic derivative, tentatively identified as 6,7,8-trihydroxy-7,8-dihydrobenzo[a]pyrene, which accounted for ～30% of the total metabolites formed by microsomes from control and phenobarbital-pretreated rats whereas this metabolite represents ～5% of the total metabolites with microsomes from 3-methylcholanthrene-treated rats. With benzo[a]pyrene as substrate, liver microsomes produced the 4,5-, 7,8- and 9,10-dihydrodiol with high optical purity (>85%), and diol epoxides were also formed. Most of the optical activity in the BP 7,8-dihydrodiol was due to metabolism by the monoxygenase system rather than by epoxide hydrase, since hydration of (±)-benzo[a]pyrene 7,8-oxide by liver microsomes produced dihydrodiol which was only 8% optically pure. Thus, the stereospecificity of both the monoxygenase system and, to a lesser extent, epoxide hydrase plays important roles in the metabolic activation of benzo[a]pyrene to carcinogens and mutagens.     

Enhancement of DNA binding,mutagenicity and carcinogenicity of polycyclic aromatic hydrocarbons after induction of cytochrome P-450 by ellipticines in rats and mice

Pretreatment of rats by ellipticines enhanced the microsomal concentration of cytochrome P-450, benzo[a]pyrene (BP) metabolism and activation and, to a smaller extent, ethoxycoumarin deethylation, but not acetanilide hydroxylation. This increased BP biotransformation was essentially due to the formation of bay-region metabolites, BP 9,10-diol, BP 7,8-diol and 9-hydroxy-BP, or to the formation of BP 7,8-diol-9,10-epoxide- and of 9-hydroxy-BP 4,5-oxide-DNA adducts. In the ellipticine series, 9-fluoroellipticine (9-FE) presents a slight inducing potency compared with the parent and 9-hydroxy molecules. Pretreatment of mice with 9-hydroxyellipticine (9-OHE) led also to an increased mutagenicity of BP and to an augmentation of skin carcinogenesis by 7,12-dimethylbenz[a]anthracene (DMBA). These results clearly show that 9-OHE induces the biosynthesis of cytochrome P-450 which markedly stimulates the mutagenic and carcinogenic potentialities of polycyclic aromatic hydrocarbons (PAH).     

Mutagenicity of non-K-region diols and diol-epoxides of benz(a)anthracene and benzo(a)pyrene in S. typhimurium TA 100

When incubated with a 9,000 x g rat-liver supernatant, benzo(a)pyrene 7,8-diol and benz(a)anthracene 8,9-diol were more active than the parent hydrocarbons in inducing his⁺ revertant colonies of S. typhimurium TA 100. Benzo(a) pyrene 9,10-diol was less active than benzo(a)pyrene; the K-region diols, benz(a)anthracene 5,6-diol and benzo(a)pyrene 4,5-diol, were inactive. None of the diols was active when the cofactors for the microsomal mono-oxygenase were omitted. The diol-epoxides benzo(a)pyrene 7,8-diol 9,10-oxide, benz(a)anthracene 8,9-diol 10,11-oxide and 7-methylbenz(a)anthracene 8,9-diol 10,11-oxide and the K-region epoxides, benzo(a)pyrene 4,5-oxide and benz(a)anthracene 5,6-oxide, were mutagenic without further metabolism.     

Formation of reactive 1-nitropyrene metabolites by lung microsomes and isolated lung cells

The metabolism and activation of 1-nitropyrene (1-NP) to reactive intermediates by lung microsomes and isolated lung cells was studied. Mutagenicity of 1-NP metabolites was assayed in Salmonella typhimurium TA98NR, a strain lacking a major component of nitroreductase activity. In the presence of NADPH, microsomes from rabbit, rat and hamster lung metabolized 1-NP to mutagenic products to a similar degree. Pretreatment with a mixture of polychlorinated biphenyls (PCB) decreased the formation of mutagenic metabolites by rabbit lung microsomes, but did not affect the production of mutagens by rat or hamster lung microsomes. ³H-1-NP was metabolized to covalently bound protein products at a rate of 82 and 10 pmol/mg by rabbit and hamster lung microsomes, respectively, whereas no binding was detected in rat lung microsomes. PCB-pretreatment increased covalent protein binding of ³ H-1-NP in lung microsomes from hamster and rat, but decreased the binding in rabbit lung microsomes. High performance liquid chromatography analysis indicated that ³H-1-NP was readily converted to ring-hydroxylated products by rabbit and hamster lung microsomes; the rate was much lower with rat lung microsomes. ³H-1-NP was activated to metabolites that covalently bound to protein in isolated rabbit lung cells, with the following rates being observed: Clara cells > lung digest > type II cells. In contrast, covalent protein binding in cells isolated from rat lung was very low. 1-NP was not activated to products mutagenic for S. typhimurium TA 98 N R when co-incubated with cells isolated either from rabbit or rat lung.Abbreviations 1-AP 1-aminopyrene - DMSO dimethyl sulfoxide - EGTA ethylene glycol-bis(ß-aminoethyl ether) - EM electron microscopy - HEPES N-2-hydroxyethylpiperazine-N'-2-ethanesulfonic acid - HPBS HEPES-phosphate-buffered-saline - HPLC high performance liquid chromatography - NBT nitroblue tetrazolium - 1-NP 1-nitropyrene - 1-NP-4,5-diol trans-4,5-dihydro-4,5-dihydroxy-1-nitropyrene - 1-NP-9,10-diol trans-9,10-dihydro-9,10-dihydroxy-1-nitropyrene - 1-NP-4,5-oxide 1-nitropyrene-4,5-oxide - 1-NP-9,10-oxide 1-nitropyrene-9,10-oxide - 3-OH-1-NP 3-hydroxy-1-nitropyrene - 6-/8-OH-1-NP a mixture of 6- and 8-hydroxy-1-nitropyrene - PBS phosphate-buffered saline - PCB a mixture of polychlorinated biphenyls (Aroclor 1254) - TLC thin layer chromatography     

Formation of DAN-binding products from isolated benzo[a]pyrene metabolites in rat liver nuclei

Liver nuclei from 3-methylcholanthrene-treated rats in the presence of NADPH metabolized 3- and 9-hydroxybenzo[a]pyrene and 7,8-dihydro-7,8-dihydroxybenzo[a]pyrene to products that bound to DNA. Maximal binding was obtained with the dihydrodiol which was approximately 3-fold that with 9-hydroxybenzo[a]pyrene, and 60-fold that with 3-hydroxybenzo[a]pyrene, as substrates. Both 4,5-dihydro-4,5-dihydroxybenzo[a]pyrene and 9,10-dihydro-9,10-dihydroxybenzo[a]pyrene were also extensively metabolized by the nuclear fraction but did not give rise to DNA-binding products.The available evidence suggests that the DNA binding species derived from 9-hydroxy-benzo[a]pyrene is 9-hydroxy-benzo[a]pyrene-4,5-oxide and from 7,8-dihydro-7,8-dihydroxybenzo[a]pyrene, as previously observed in different systems, 7,8-dihydro-7,8-dihydroxy-benzo[a]pyrene-9,10-oxide.     

Metabolic activation of benzo[a]pyrene in human skin maintained in short-term organ culture

The metabolic activation of benzo[a]pyrene (BP) was examined in six samples of human skin after topical application of the hydrocarbon to the skin in short-term organ culture. The results show that all of the samples were capable of metabolizing BP to water-soluble products and to ether-soluble products that included the 4,5-, 7,8- and 9,10-dihydrodiols and a product which had chromatographic properties identical with those of authentic trans-11,12-dihydro-11,12-dihydroxybenzo[a]pyrene (BP-11,12-diol). The major BP-deoxyribonucleoside adduct detected in each skin sample appeared to be formed from the reaction of r-7,t-8-dihydroxy-t-9,10-oxy-7,8,9,10-tetrahydrobenzo[a]pyrene (anti-BP-7,8-diol 9,10-oxide) with deoxyguanosine residues in DNA.     

Epoxy derivatives of aromatic polycyclic hydrocarbons. The preparation and metabolism of epoxides related to benzo[a]pyrene and to 7,8- and 9,10-dihydrobenzo[a]pyrene

Products that appeared to be mainly benzo[a]pyrene 7,8-oxide and benzo[a]pyrene 9,10-oxide were synthesized and their chemical and biochemical properties were investigated. The oxides were unstable and readily rearranged to phenols. They were converted by rat liver homogenates and microsomal preparations into phenols and dihydrodiols, but glutathione conjugates were not formed in appreciable amounts. The dihydrodiols formed from benzo[a]pyrene 7,8- and 9,10-oxide by rat liver microsomal preparations were identical in their chromatographic and spectrographic properties with dihydrodiols formed when benzo[a]pyrene was metabolized by rat liver homogenates. 9,10-Dihydrobenzo[a]pyrene 7,8-oxide and 7,8-dihydrobenzo[a]pyrene 9,10-oxide were also synthesized. They were converted by rat liver homogenates and microsomal preparations into the related cis- and trans-dihydroxy compounds. Glutathione conjugates were formed from the oxides by rat liver homogenates. Both 7,8- and 9,10-dihydrobenzo[a]pyrene were metabolized by rat liver homogenates to mainly the trans-isomers of the related dihydroxy compounds. In experiments with boiled homogenates, the benzo[a]pyrene oxides were converted into phenols, whereas the dihydrobenzo[a]pyrene oxides yielded small amounts of the related dihydroxy compounds.     

Postreplication repair of DNA in human fibroblasts after UV irradiation or treatment with metabolites of benzo(a)pyrene

We have examined the ability of normal fibroblasts and of excision-deficient xeroderma pigmentosum (XP) and XP variant fibroblasts to perform postreplication DNA repair after increasing doses of either ultraviolet (UV) irradiation or mutagenic benzo(a)pyrene derivatives. XP cells defective in the excision of both UV-induced pyrimidine dimers and guanine adducts induced by treatment with the 7,8-diol-9,10-epoxides of benzo(a)pyrene were partially defective in their ability to synthesize high molecular weight DNA after the induction of both classes of DNA lesions. This defect was more marked in XP variant cells, despite their ability to remove by excision repair both pyrimidine dimers and the diol epoxide-induced lesions to the same degree as observed in normal cells. The benzo(a)pyrene 9,10-oxide had no effect in any of the 3 cell lines. The response of the excision and postreplication DNA repair mechanisms operating in human fibroblasts treated with benzo(a)pyrene 7,8-diol-9,10-epoxides, therefore, appears to resemble closely that seen after the induction of pyrimidine dimers by UV irradiation.     

Glucuronidation of benzo[a]pyrene in hamster embryo cells

The formation of water-soluble metabolites of tritium-labeled benzo[a]pyrene (BP) by cultured hamster embryo cells was studied. The ratio of the radioactivity in the aqueous phase to that in the organic phase increased with the incubation period. After incubation for 48 h with 3.75 nmol/ml of [3H] BP in the medium more than 90% of the 3H-radioactivity was found in the aqueous phase, whereas with 10-fold more BP about half the radioactivity remained in the organic phase. The main metabolites extracted from the medium at 37.5 nmol/ml BP with ethyl acetate by high pressure liquid chromatography (HPLC) were 9,10-diol and 7,8-diol; but after treatment of the medium with beta-glucuronidase the main oxygenated metabolites were phenols, the amount of 9-OH BP being more than that of 3-OH BP. beta-Glucuronidase also released 9,10-diol and 7,8-diol, but most of these diols were in the free form in the medium. The medium from cells treated with 3.75 nmol/ml BP has a quantitatively different profile, and most of the radioactivity obtained by extraction with organic solvent and digestion with beta-glucuronidase was eluted in the regions of phenols. These results show that in hamster embryo cells BP is mainly metabolised to conjugates of phenols with glucuronic acid.     

Metabolism of benzo(a)pyrene by human lung microsomal fractions

The metabolism of benzo(a)pyrene was studied using microsomal fractions obtained from human lung derived at either resection or autopsy. The rates of metabolism and metabolite distribution were monitored using high pressure liquid chromatography and the metabolic rates were noted to be similar to those obtained using rat lung microsomes. In contrast to the rat, human lung microsomes appear to form a higher percentage of the 7,8-dihydro-7, 8-diol or 9,10-dihydro-9, 10-diol of benzo(a)pyrene as a fraction of the total metabolites. However, there was a significant variation among the human lung microsomal preparations which might reflect the clinical diagnosis and/or individual variation.     

The effect of manganese and ferric ions on the in vitro formation of dihydrodihydroxy metabolites of benzo(a)pyrene

The effect of ferric and manganese ions on the in vitro metabolism of benzo(a)pyrene (BP) to dihydrodihydroxy (diol) metabolites by rat liver microsomal preparations was studied. Of the 3 diols separated by high-pressure liquid chromatography (HPLC) and called diols 1, 2 and 3 in order of elution, diol 1 was identified by its U.V. spectrum as the 9,10-diol; diols 2 and 3 have not yet been identified positively but are probably the 4,5- and 7,8-diols respectively. Higher concentrations of both metals altered the diol profile; 10 and 50 mumol Fe3+ per incubation caused the disappearance of diols 1 and 2 and an increase in diol 3; 10 mumol Mn2+ caused a significant decrease in diol 2 while 50 mumol reduced diol 2 to a negligible amount and inhibited the formation of diol 1; both concentrations caused a relative increase in diol 3. If the tentative identification of diol 3 as the 7,8-diol is correct, manganese and ferric ions could be significant in the metabolism of BP to the active metabolite, the 7,8-diol-9,10-epoxide.     

Dual-label high-performance liquid chromatographic assay for femtomole levels of benzo[a]pyrene metabolites

A dual-label HPLC assay to measure femtomole quantities of ethyl acetate-extractable [3H]benzo[a]pyrene metabolites was developed. 14C-labeled metabolites of benzo[a]pyrene formed by rat liver 9000g supernatant were used as both internal standards and chromatographic markers. The percentage deviation between assays was determined to be between 11 and 13% for 9,10-dihydro-9,10-dihydroxybenzo[a]pyrene, 7,8-dihydro-7,8-dihydroxybenzo[a]pyrene, benzo[a]pyrene-3,6-quinone, benzo[a]pyrene-1,6-quinone, and 9-hydroxybenzo[a]pyrene, 22% for 4,5-dihydro-4,5-dihydroxybenzo[a]pyrene, and less than 5% for 3-hydroxybenzo[a]pyrene. The detection limit of this assay was between 3 and 10 fmol per metabolite. The application of this technique to the metabolism of [3H]benzo[a]pyrene by microsomes of hamster and human oral cavity tissue is described.     

Product inhibition of benzo[a]pyrene metabolism in uninduced rat liver microsomes: Effect of diol epoxide formation

Conversion of benzo[a]pyrene (BP) to BP 7,8-dihydrodiol 9,10-oxides (DE) (measured as 7,10/8,9-tetrols) by untreated (UT) rat liver microsomes is over 10 times slower than following 3-methylcholanthrene (MC) induction. Time courses have been subjected to a kinetic analysis analogous to that previously reported for metabolism by MC-induced microsomes (J. Biol. Chem., 259 (1984) 13770–13776). Competition between BP and 7,8-dihydrodiol for P-450 is the major determinant of the rate of DE formation. Glucuronidation of quinones and phenols only increases the isolated BP metabolites including DE by 40%. This indicates far less inhibition by these products than for metabolism in MC-microsomes (4–6-fold). Thus stimulation may result from a decreased quinone-mediated oxidation of metabolites. In the presence of DNA, UT-microsomes metabolize BP to approximately equal amounts of 9-phenol-4,5-oxide (9-PO) and DE/DNA adducts. Addition of uridine diphosphoglucuronic acid (UDPGA) fails to enhance modification of DNA by DE, but formation of the 9-PO adduct is reduced as a result of lower free 9-phenol levels. The kinetic characteristics of BP metabolism by UT-microsomes are highly sensitive to the presence of very small but variable amounts (2–25 pmol/mg) of the very active cytochrome P-450_c, which is the predominant form in MC-microsomes. The major effect of elevated levels of P-450_c is an 8-fold increase in DE formation at low concentrations of BP due to a lowering of K_m (7.9–2.6 μM) and an increase in the regioselectivity for DE formation from 7,8-dihydrodiol (5–15% of total BP metabolites). The formation of DE was directly correlated with the content of P-450_c (r = 0.94). The presence of increased levels of P-450_c in UT-microsomes is probably due to previous exposure of the animals to environmental inducers and is minimized by controlled housing and feeding.