Monooxygenase, peroxidase and peroxygenase properties and reaction mechanisms of cytochrome P450 enzymes.

This review examines the monooxygenase, peroxidase and peroxygenase properties and reaction mechanisms of cytochrome P450 (CYP) enzymes in bacterial, archaeal and mammalian systems. CYP enzymes catalyze monooxygenation reactions by inserting one oxygen atom from O2 into an enormous number and variety of substrates. The catalytic versatility of CYP stems from its ability to functionalize unactivated carbon-hydrogen (C-H) bonds of substrates through monooxygenation. The oxidative prowess of CYP in catalyzing monooxygenation reactions is attributed primarily to a porphyrin π radical ferryl intermediate known as Compound I (CpdI) (Por•+FeIV=O), or its ferryl radical resonance form (FeIV-O•). CYP-mediated hydroxylations occur via a consensus H atom abstraction/oxygen rebound mechanism involving an initial abstraction by CpdI of a H atom from the substrate, generating a highly-reactive protonated Compound II (CpdII) intermediate (FeIV-OH) and a carbon-centered alkyl radical that rebounds onto the ferryl hydroxyl moiety to yield the hydroxylated substrate. CYP enzymes utilize hydroperoxides, peracids, perborate, percarbonate, periodate, chlorite, iodosobenzene and N-oxides as surrogate oxygen atom donors to oxygenate substrates via the shunt pathway in the absence of NAD(P)H/O2 and reduction-oxidation (redox) auxiliary proteins. It has been difficult to isolate the historically elusive CpdI intermediate in the native NAD(P)H/O2-supported monooxygenase pathway and to determine its precise electronic structure and kinetic and physicochemical properties because of its high reactivity, unstable nature (t½~2 ms) and short life cycle, prompting suggestions for participation in monooxygenation reactions of alternative CYP iron-oxygen intermediates such as the ferric-peroxo anion species (FeIII-OO-), ferric-hydroperoxo species (FeIII-OOH) and FeIII-(H2O2) complex.

The monooxygenase, peroxidase, and peroxygenase properties of cytochrome P450.

This review examines the monooxygenase, peroxidase, and peroxygenase properties of cytochrome P450 (P450)1 enzymes and their mechanisms of action in archaeal, bacterial, and mammalian systems. In the P450 catalytic cycle, a transient iron oxo monooxygenating species is generated that reacts with substrate to produce a monooxygenated product. We describe results of early investigations that endeavored to trap and detect this elusive monooxygenating species, as well as results of experiments that attempted to generate and characterize this active oxidant spectroscopically after reacting ferric P450 enzymes with peroxy compounds (e.g. peroxides, peracids) or single oxygen atom donors (e.g. periodate, iodosobenzene). Surrogate oxidants were able to promote P450-catalyzed monooxygenations in a manner similar to that of O2/NAD(P)H, suggesting involvement of a common transitory monooxygenating species in the two pathways. This common P450 oxidant was characterized as a porphyrin radical iron(IV) oxo complex and assigned a Compound I structure (Por+FeIV=O) exhibiting a formal FeV oxidation state. Other reactive oxidants, such as the ferric oxenoid complex (PorFeIII=O), ferryloxy radical species (PorFeIV-O·), and perferryloxo entity (PorFeV=O), were also proposed to function as P450 monooxygenating species. We also discuss the possible involvement of the ferriperoxo (PorFeIII-OO-) and ferrihydroperoxo (PorFeIII-OOH) species as alternative oxidants in P450-mediated monooxygenation reactions.

2,2',3,3',6,6'-Hexachlorobiphenyl (PCB 136) is enantioselectively oxidized to hydroxylated metabolites by rat liver microsomes.

Developmental exposure to multiple ortho-substituted polychlorinated biphenyls (PCBs) causes adverse neurodevelopmental outcomes in laboratory animals and humans by mechanisms involving the sensitization of Ryanodine receptors (RyRs). In the case of PCB 136, the sensitization of RyR is enantiospecific, with only (-)-PCB 136 being active. However, the role of enantioselective metabolism in the developmental neurotoxicity of PCB 136 is poorly understood. The present study employed hepatic microsomes from phenobarbital (PB)-, dexamethasone (DEX)- and corn oil (VEH)-treated male Sprague-Dawley rats to investigate the hypothesis that PCB 136 atropisomers are enantioselectively metabolized by P450 enzymes to potentially neurotoxic, hydroxylated PCB 136 metabolites. The results demonstrated the time- and isoform-dependent formation of three metabolites, with 5-OH-PCB 136 (2,2',3,3',6,6'-hexachlorobiphenyl-5-ol) being the major metabolite. The formation of 5-OH-PCB 136 increased with the activity of P450 2B enzymes in the microsomal preparation, which is consistent with PCB 136 metabolism by rat P450 2B1. The minor metabolite 4-OH-PCB 136 (2,2',3,3',6,6'-hexachlorobiphenyl-4-ol) was produced by a currently unidentified P450 enzyme. An enantiomeric enrichment of (-)-PCB 136 was observed in microsomal incubations due to the preferential metabolism of (+)-PCB 136 to the corresponding 5-OH-PCB 136 atropisomer. 4-OH-PCB 136 displayed an enrichment of the atropisomer formed from (-)-PCB 136; however, the enrichment of this metabolite atropisomer did not affect the enantiomeric enrichment of the parent PCB because 4-OH-PCB 136 is only a minor metabolite. Although the formation of 5- and 4-OH-PCB 136 atropisomers increased with time, the enantioselective formation of the OH-PCB metabolites resulted in constant enantiomeric enrichment, especially at later incubation times. These observations not only demonstrate that the chiral signatures of PCBs and their metabolites in wildlife and humans are due to metabolism by P450 enzymes but also suggest that the enantioselective formation of neurotoxic PCB 136 metabolites, such as 4-OH-PCB 136, may play a role in the developmental neurotoxicity of PCBs.

2,2',3,3',6,6'-Hexachlorobiphenyl (PCB 136) atropisomers interact enantioselectively with hepatic microsomal cytochrome P450 enzymes.

2,2',3,3',6,6'-Hexachlorobiphenyl (PCB 136) is a chiral and highly neurotoxic PCB congener of environmental relevance. (+)-PCB 136 was previously shown to be enriched in tissues from mice treated with racemic PCB 136. We investigated the spectral interactions of (+)-, (-)-, and (+/-)-PCB 136 with mouse and rat hepatic microsomal cytochrome P450 (P450) enzymes to test the hypothesis that enantioselective binding to specific P450 enzymes causes the enrichment of (+)-PCB 136 in vivo. Hepatic microsomes prepared from C57BL/6 mice or Long Evans rats treated with beta-naphthoflavone or 3-methylcholanthrene, phenobarbital, and dexamethasone (prototypical inducers of CYP1A, CYP2B, and CYP3A, respectively) were used to determine first, whether the (+)-PCB 136 atropisomer binds to hepatic microsomal P450 enzymes to a greater extent than does the (-)-PCB 136 atropisomer and second, whether P450 enzymes of one subfamily bind the two PCB 136 atropisomers more efficiently than do P450 enzymes of other subfamilies. Increasing concentrations of (+)-, (-)-, or (+/-)-PCB 136 were added to hepatic microsomes, and the difference spectrum and maximal absorbance change, a measure of PCB binding to P450 enzymes, were measured. A significantly larger absorbance change was observed with (+)-PCB 136 than with (-)-PCB 136 with all four hepatic microsomal preparations in mice and rats, indicating that (+)-PCB 136 interacted with microsomal P450 enzymes to a greater degree than did (-)-PCB 136. In addition, binding of the PCB 136 atropisomers was greatest in microsomes from PB-treated mice and rats and was inhibited by CYP2B antibodies, indicating the involvement of CYP2B enzymes. Together, these results suggest preferential binding of (+)-PCB 136 to P450 enzymes (such as CYP2B and CYP3A) in hepatic microsomes, an observation that may explain the enantioselective enrichment of the (+)-PCB 136 atropisomer in tissues of mice.

Differential inhibition of hepatic microsomal alkoxyresorufin O-dealkylation activities by tetrachlorobiphenyls.

Polychlorinated biphenyls (PCBs) elicit a spectrum of biochemical and toxic effects in exposed animals. In the present study, we assessed the effect of PCB structure, using four symmetrically-substituted PCBs, on cytochrome P450 (CYP)-mediated methoxy-, ethoxy- and benzyloxyresorufin O-dealkylase (MROD, EROD and BROD, respectively) activities. We found that 2,2',4,4'-tetrachlorobiphenyl (PCB 47), 2,2',5,5'-tetrachlorobiphenyl (PCB 52), 2,2',6,6'-tetrachlorobiphenyl (PCB 54) and 3,3',4,4'-tetrachlorobiphenyl (PCB 77) inhibited alkoxyresorufin O-dealkylase activities in hepatic microsomes from 3-methylcholanthrene (MC) or phenobarbital (PB)-treated rats. Measurement of the in vitro inhibitory potencies of the tetrachlorobiphenyls revealed that MROD, EROD and BROD activities were differentially inhibited and the degree of inhibition was determined by the chlorination pattern of the PCB. PCB 77 was more potent than PCB 47 or PCB 52 at inhibiting MROD and EROD activities in hepatic microsomes from MC-treated rats, while no inhibition of either activity was observed with PCB 54. In contrast, BROD activity measured in hepatic microsomes from PB-treated rats was inhibited by PCB 47, PCB 52 and PCB 54 but not by PCB 77. The mode of inhibition for each activity was also evaluated statistically. Inhibition of the alkoxyresorufin O-dealkylase activities could not be discerned in hepatic microsomes from corn oil-treated rats because the activities were inherently too low. No evidence for mechanism-based inhibition of MROD, EROD or BROD activities or an effect via CYP reductase was found. The results demonstrate that relatively coplanar PCBs such as PCB 77 preferentially inhibit EROD and MROD activities, whereas noncoplanar PCBs such as PCB 54 preferentially inhibit BROD activity.

Involvement of Cytochrome P450 in Reactive Oxygen Species Formation and Cancer.

This review examines the involvement of cytochrome P450 (CYP) enzymes in the formation of reactive oxygen species in biological systems and discusses the possible involvement of reactive oxygen species and CYP enzymes in cancer. Reactive oxygen species are formed in biological systems as byproducts of the reduction of molecular oxygen and include the superoxide radical anion (∙O2-), hydrogen peroxide (H2O2), hydroxyl radical (∙OH), hydroperoxyl radical (HOO∙), singlet oxygen ((1)O2), and peroxyl radical (ROO∙). Two endogenous sources of reactive oxygen species are the mammalian CYP-dependent microsomal electron transport system and the mitochondrial electron transport chain. CYP enzymes catalyze the oxygenation of an organic substrate and the simultaneous reduction of molecular oxygen. If the transfer of oxygen to a substrate is not tightly controlled, uncoupling occurs and leads to the formation of reactive oxygen species. Reactive oxygen species are capable of causing oxidative damage to cellular membranes and macromolecules that can lead to the development of human diseases such as cancer. In normal cells, intracellular levels of reactive oxygen species are maintained in balance with intracellular biochemical antioxidants to prevent cellular damage. Oxidative stress occurs when this critical balance is disrupted. Topics covered in this review include the role of reactive oxygen species in intracellular cell signaling and the relationship between CYP enzymes and cancer. Outlines of CYP expression in neoplastic tissues, CYP enzyme polymorphism and cancer risk, CYP enzymes in cancer therapy and the metabolic activation of chemical procarcinogens by CYP enzymes are also provided.

Spectral interactions of tetrachlorobiphenyls with hepatic microsomal cytochrome p450 enzymes.

This study investigated the spectral interactions of hepatic microsomal cytochrome p450 (CYP) enzymes with four symmetrical polychlorinated biphenyls (PCBs): 2,2',4,4'-tetrachlorobiphenyl (PCB 47); 2,2',5,5'-tetrachlorobiphenyl (PCB 52); 2,2',6,6'-tetrachlorobiphenyl (PCB 54); and 3,3',4,4'-tetrachlorobiphenyl (PCB 77). The PCBs were selected to explore structure-activity relationships and the effect of the chlorination pattern on PCB-CYP spectral interactions. To examine CYP enzyme specificity, difference spectra were measured with hepatic microsomes prepared from control, phenobarbital (PB)-, 3-methylcholanthrene (MC)-, and dexamethasone (DEX)-treated rats in the absence and presence of CYP-specific antibodies. The four PCB congeners elicited a type I spectral change with all hepatic microsomal preparations. The binding efficiency of the PCBs was highest with microsomes from PB-treated rats. The largest absorbance change and highest binding efficiency were observed with PCB 54, the most non-coplanar congener tested. Antibody inhibition and CYP immunoquantitation data showed that the PCBs bind to CYP1A, CYP2B, CYP2C and CYP3A enzymes to varying degrees. For example, PCB 47, 52, and 54 bind preferentially to CYP2B and to a lesser extent to CYP3A enzymes in microsomes from PB-treated male rats; PCB 52 binds primarily to CYP3A enzymes in microsomes from DEX-treated female rats; and PCB 54 binds to CYP3A and to CYP2C enzymes in microsomes from control male rats. The study demonstrated that the extent of PCB-CYP binding interaction was dependent on the chlorination pattern of the PCB and on the relative abundance of individual CYP enzymes in hepatic microsomes.

Lipid reserve dynamics and magnification of persistent organic pollutants in spawning sockeye salmon (Oncorhynchus nerka) from the Fraser River, British Columbia.

Pacific sockeye salmon (Oncorhynchus nerka) can travel several hundred kilometers to reach native spawning grounds and fulfill semelparous reproduction. The dramatic changes in lipid reserves during upstream migration can greatly affect internal toxicokinetics of persistent organic pollutants (POPs) such as PCBs, PCDDs, and PCDFs. We measured lipid content changes and contaminant concentrations in tissues (liver, muscle, roe/gonads) and biomarker responses (ethoxyresorufin O-deethylase or EROD activity and CYP1A levels) in two Pacific sockeye salmon stocks sampled at several locations along their spawning migration in the Fraser River, British Columbia. Muscle lipid contents declined significantly with increasing upstream migration distance and corresponded to elevated lipid normalized concentrations of PCBs and PCDD/Fs in spawning sockeye. Post-migration magnification factors (MFs) in spawning sockeye ranged between 3 and 12 and were comparable to model-predicted MFs. sigmaPCBs(150-500 ng x g(-1) lipid), sigmaPCDD/Fs (1-1000 pg x g(-1) lipid) and 2,3,7,8-TCDD toxic equivalent or TEQ levels (0.1-15 pg x g(-1) lipid) in spawning sockeye were relatively low and did not affect hepatic EROD activity/CYP1A induction. Despite a 3-fold magnification, TEQ levels in eggs of spawning Fraser River sockeye did not exceed 0.3 pg x g(-1) wet wt, a threshold level associated with 30% egg mortality in salmonids. PCBs in Fraser River sockeye are comparable to previous levels in Pacific sockeye. In contrast to Pacific sockeye from more remote coastal locations, PCDDs and PCDFs in Fraser River sockeye were generally minor components (<25%) of TEQ levels, compared to dioxin like PCB contributions (>75%). The data suggest that (i) the Fraser River is not a major contamination source of PCBs or PCDD/Fs and (ii) marine contaminant distribution, food-chain dynamics, and ocean-migration pathway are likely important factors controlling levels and patterns of POPs in returning Pacific sockeye. We estimate an annual chemical flux entering the Fraser River of up to 150 g for sigmaPCBs and 40 mg for sigmaPCDD/ Fs via returning sockeye. The results indicate that historical concentrations of PCBs and PCDD/Fs remain a potential threat to organism and ecosystem health on the west coast of Canada.