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Naphthalene, phenanthrene, biphenyl, and their derivatives having different ethynyl, propynyl, butynyl, and propargyl ether substitutions were examined for their interaction with and oxidation by cytochromes P450 (P450) 2A13 and 2A6. Spectral interaction studies suggested that most of these chemicals interacted with P450 2A13 to induce Type I binding spectra more readily than with P450 2A6. Among the various substituted derivatives examined, 2-ethynylnaphthalene, 2-naphthalene propargyl ether, 3-ethynylphenanthrene, and 4-biphenyl propargyl ether had larger ΔAmax/Ks values in inducing Type I binding spectra with P450 2A13 than their parent compounds. P450 2A13 was found to oxidize naphthalene, phenanthrene, and biphenyl to 1-naphthol, 9-hydroxyphenanthrene, and 2- and/or 4-hydroxybiphenyl, respectively, at much higher rates than P450 2A6. Other human P450 enzymes including P450s 1A1, 1A2, 1B1, 2C9, and 3A4 had lower rates of oxidation of naphthalene, phenanthrene, and biphenyl than P450s 2A13 and 2A6. Those alkynylated derivatives that strongly induced Type I binding spectra with P450s 2A13 and 2A6 were extensively oxidized by these enzymes upon analysis with HPLC. Molecular docking studies supported the hypothesis that ligand-interaction energies (U values) obtained with reported crystal structures of P450 2A13 and 2A6 bound to 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone, indole, pilocarpine, nicotine, and coumarin are of use in understanding the basis of possible molecular interactions of these xenobiotic chemicals with the active sites of P450 2A13 and 2A6 enzymes. In fact, the ligand-interaction energies with P450 2A13 4EJG bound to these chemicals were found to relate to their induction of Type I binding spectra.

Human cytochrome P450 (P450) 2A13 was found to interact with several polycyclic aromatic hydrocarbons (PAHs) to produce Type I binding spectra, including acenaphthene, acenaphthylene, benzo[c]phenanthrene, fluoranthene, fluoranthene-2,3-diol, and 1-nitropyrene. P450 2A6 also interacted with acenaphthene and acenaphthylene, but not with fluoranthene, fluoranthene-2,3-diol, or 1-nitropyrene. P450 1B1 is well known to oxidize many carcinogenic PAHs, and we found that several PAHs (i.e., 7,12-dimethylbenz[a]anthracene, 7,12-dimethylbenz[a]anthracene-5,6-diol, benzo[c]phenanthrene, fluoranthene, fluoranthene-2,3-diol, 5-methylchrysene, benz[a]pyrene-4,5-diol, benzo[a]pyrene-7,8-diol, 1-nitropyrene, 2-aminoanthracene, 2-aminofluorene, and 2-acetylaminofluorene) interacted with P450 1B1, producing Reverse Type I binding spectra. Metabolic activation of PAHs and aryl- and heterocyclic amines to genotoxic products was examined in Salmonella typhimurium NM2009, and we found that P450 2A13 and 2A6 (as well as P450 1B1) were able to activate several of these procarcinogens. The former two enzymes were particularly active in catalyzing 2-aminofluorene and 2-aminoanthracene activation, and molecular docking simulations supported the results with these procarcinogens, in terms of binding in the active sites of P450 2A13 and 2A6. These results suggest that P450 2A enzymes, as well as P450 Family 1 enzymes including P450 1B1, are major enzymes involved in activating PAHs and aryl- and heterocyclic amines, as well as tobacco-related nitrosamines.

A total of 68 chemicals including derivatives of naphthalene, phenanthrene, fluoranthene, pyrene, biphenyl, and flavone were examined for their abilities to interact with human P450s 2A13 and 2A6. Fifty-one of these 68 chemicals induced stronger Type I binding spectra (iron low- to high-spin state shift) with P450 2A13 than those seen with P450 2A6, i.e., the spectral binding intensities (ΔAmax/Ks ratio) determined with these chemicals were always higher for P450 2A13. In addition, benzo[c]phenanthrene, fluoranthene, 2,3-dihydroxy-2,3-dihydrofluoranthene, pyrene, 1-hydroxypyrene, 1-nitropyrene, 1-acetylpyrene, 2-acetylpyrene, 2,5,2',5'-tetrachlorobiphenyl, 7-hydroxyflavone, chrysin, and galangin were found to induce a Type I spectral change only with P450 2A13. Coumarin 7-hydroxylation, catalyzed by P450 2A13, was strongly inhibited by 2'-methoxy-5,7-dihydroxyflavone, 2-ethynylnaphthalene, 2'-methoxyflavone, 2-naphththalene propargyl ether, acenaphthene, acenaphthylene, naphthalene, 1-acetylpyrene, flavanone, chrysin, 3-ethynylphenanthrene, flavone, and 7-hydroxyflavone; these chemicals induced Type I spectral changes with low Ks values. On the basis of the intensities of the spectral changes and inhibition of P450 2A13, we classified the 68 chemicals into eight groups based on the order of affinities for these chemicals and inhibition of P450 2A13. The metabolism of chemicals by P450 2A13 during the assays explained why some of the chemicals that bound well were poor inhibitors of P450 2A13. Finally, we compared the 68 chemicals for their abilities to induce Type I spectral changes of P450 2A13 with the Reverse Type I binding spectra observed with P450 1B1: 45 chemicals interacted with both P450s 2A13 and 1B1, indicating that the two enzymes have some similarty of structural features regarding these chemicals. Molecular docking analyses suggest similarities at the active sites of these P450 enzymes. These results indicate that P450 2A13, as well as Family 1 P450 enzymes, is able to catalyze many detoxication and activation reactions with chemicals of environmental interest.

Human cytochrome P450s 1A1, 1A2, and 1B1 are known to have overlapping substrate specificities. All are regulated in part by the Ah locus; P450 1A2 is expressed essentially only in liver, but P450s 1A1 and 1B1 are both expressed in many extrahepatic tissues. Twenty-five polycyclic hydrocarbons, many containing acetylenic side chains, were examined as inhibitors of the three enzymes using 7-ethoxyresorufin O-deethylation as the enzyme assay in all cases. Several compounds were inhibitory at low nanomolar concentrations. 1-(1-Propynyl)pyrene and 2-(1-propynyl)phenanthrene nearly completely inhibited P450 1A1 at concentrations at which no P450 1B1 inhibition was observed. 2-Ethynylpyrene and alpha-naphthoflavone (7, 8-benzoflavone) nearly completely inhibited P450 1B1 at concentrations at which no P450 1A1 inhibition was noted. All four of the above compounds also inhibited P450 1A2. Several polycyclic hydrocarbons devoid of acetylenic groups were also inhibitory with respect to all three P450s. Some of the acetylenic compounds examined showed enhanced inhibition following preincubation with the P450s in the presence of cofactors NADPH and O2. However, of seven compounds (five acetylenes) tested with P450 1B1, only two [2-ethynylpyrene and 4-(1-propynyl)biphenyl] showed such evidence for mechanism-based inactivation. We conclude that (i) several polycyclic hydrocarbons and their oxidation products are very inhibitory with respect to human P450s 1A1, 1A2, and 1B1; (ii) of these inhibitors only some are mechanism-based inactivators; and (iii) some of the inhibitors are potentially useful for distinguishing between human P450s 1A1 and 1B1.

Of seven cDNA-expressed human cytochrome P450 (P450) enzymes (P450s 1A2, 2B6, 2C9, 2C19, 2D6, 2E1, and 3A4) examined, P450 1A2 was the most active in catalyzing 2- and 4-hydroxylations of estradiol and estrone. P450 3A4 and P450 2C9 also catalyzed these reactions although to lesser extents than P450 1A2. P450 1A2 also efficiently oxidized estradiol at the 16alpha-position but was less active in estrone 16alpha-hydroxylation; the latter reaction and also estradiol 16alpha-hydroxylation were catalyzed by P450 3A4 at significant levels. Anti-P450 1A2 antibodies inhibited 2- and 4-hydroxylations of these two estrogens catalyzed by liver microsomes of some of the human samples examined. Estradiol 16alpha-hydroxylation was inhibited by both anti-P450 1A2 and anti-P450 3A4, while estrone 16alpha-hydroxylation was significantly suppressed by anti-P450 3A4 in human liver microsomes. Fluvoxamine efficiently inhibited the estrogen hydroxylations in human liver samples that contained high levels of P450 1A2, while ketoconazole affected these activities in human samples in which P450 3A4 levels were high. alpha-Naphthoflavone either stimulated or had no effect on estradiol hydroxylation catalyzed by liver microsomes; the intensity of this effect depended on the human samples and their P450s. Interestingly, in the presence of anti-P450 3A4 antibodies, alpha-naphthoflavone was found to be able to inhibit estradiol and estrone 2-hydroxylations catalyzed by human liver microsomes. The results suggest that both P450s 1A2 and 3A4 have major roles in oxidations of estradiol and estrone in human liver and that the contents of these two P450 forms in liver microsomes determine which P450 enzymes are most important in hepatic estrogen hydroxylation by individual humans. P450 3A4 may be expected to play a more important role for some of the estrogen hydroxylation reactions than P450 1A2. Knowledge of roles of individual P450s in these estrogen hydroxylations has relevance to current controversies in hormonal carcinogenesis [Service, R. F. (1998) Science 279, 1631-1633].

Aflatoxin B1 (AFB1) must be activated to the electrophilic AFB1 exo-8,9-epoxide to be genotoxic and carcinogenic. A role for epoxide hydrolase in detoxication has been suggested but never directly addressed. In light of recent studies determining the instability of AFB1 exo-8,9-epoxide in H2O, a role for epoxide hydrolase appears dubious. Rat liver or recombinant rat epoxide hydrolase provided an enhancement to the already fast hydrolysis rate of up to 22%. Purified human epoxide hydrolase provided no detectable enhancement to the rate of chemical hydrolysis. Some reduction in the genotoxicity of AFB1 was observed when the ratio of rat epoxide hydrolase to cytochrome P450 was high (approximately 50-fold). An 80-fold excess of human epoxide hydrolase over cytochrome P450 only produced an effect of approximately 25% inhibition. It appears, therefore, that there is little evidence to support a role for epoxide hydrolase in the detoxication of AFB1.

Recombinant cytochrome P450 (P450) 3A4 was most active in nifedipine and testosterone oxidation in a system including NADPH-P450 reductase, cytochrome b5 (b5), a semisynthetic phospholipid mixture plus cholate, glutathione, and MgCl2. The MgCl2 effect could be seen with high concentrations of Ca2+ or Sr2+ but not readily when these cations were replaced with monovalent cations. The divalent cation effect was also seen in liver microsomes. Part of the basis of this effect appears to be enhanced rates of b5 reduction, as judged from studies on deletions of reconstitution components and analysis of steady-state spectral studies. Rapid reduction of ferric P450 3A4 to ferrous was dependent upon the presence of substrate, either testosterone or ethylmorphine. When testosterone was present, reduction was also highly dependent upon the presence of b5 and Mg2+. In the case of the substrate ethylmorphine, the need to add b5 and Mg2+ to obtain optimal reduction rates was less pronounced. These patterns are consistent with the dramatic dependence of testosterone 6 beta-hydroxylation on b5 and the lack of dependence of ethylmorphine N-demethylation on b5. Our interpretation is that divalent cations stimulate electron transfer from NADPH-P450 reductase to several acceptors and that substrates and b5 can bind to P450 3A4 to influence its rate of reduction by the reductase. P450 3A4 catalyzed testosterone 6 beta-hydroxylation within Escherichia coli cells. The reactions could be supported by E. coli cytosol or by purified E. coli flavodoxin and NADPH-flavodoxin reductase. Spinach ferredoxin and NADPH-ferredoxin reductase also supported catalytic activities.(ABSTRACT TRUNCATED AT 250 WORDS)