Study of P450 function using gene knockout and transgenic mice

The xenobiotic-metabolizing P450s have been extensively studied for their ability to metabolize endogenous and exogenous chemicals. The latter include drugs and dietary and environmentally derived toxicants and carcinogens. These enzymes also metabolize endogenous steroids and fatty acids. P450s are thought to be required for efficient removal of most xenobiotics from the body and to be responsible for the hazardous effects of toxicants and carcinogens based on their ability to convert chemicals to electrophilic metabolites that can cause cellular damage and gene mutations. P450 catalytic activities have been extensively studied in vitro and in cell culture, yielding considerable information on their mechanisms of catalysis, substrate specificities, and metabolic products. Targeted gene disruption has been used to determine the roles of P450s in intact animals and their contributions to the mechanisms of toxicity and carcinogenesis. The P450s chosen for study, CYP1A1, CYP1B1, CYP1A2, and CYP2E1, are conserved in mammals and are known to metabolize most toxicants and chemical carcinogens. Mice lacking expression of these enzymes do not differ from wild-type mice, indicating that these P450s are not required for development and physiological homeostasis. However, the P450 null mice have altered responses to the toxic and carcinogenic effects of chemicals as compared with wild-type mice. These studies establish that P450s mediate the adverse effects of drugs and dietary, environmental, and industrial chemicals and serve to validate molecular epidemiology studies that seek to determine links between P450 polymorphisms and susceptibility to chemically associated diseases. More recently, P450 humanized mice have been produced.     

Activation of microsomal epoxide hydrolase by interaction with cytochromes P450: kinetic analysis of the association and substrate-specific activation of epoxide hydrolase function

The kinetics of the association between cytochrome P450 (P450) and microsomal epoxide hydrolase (mEH) was studied by means of resonant mirror based on the principle of surface plasmon resonance. The dissociation equilibrium constants (K(D)) for the affinity of P450 enzymes for mEH were estimated by resonant mirror using an optical biosensor cell covalently bound to rat mEH. Comparable K(D) values were obtained for CYP1A1 and 2B1, and these were greater by one order of magnitude than that for the CYP2C11. To clarify the influences of P450 enzymes on the catalytic activity of mEH, the hydrolyzing activity for styrene oxide and benzo(a)pyrene-7,8-oxide [B(a)P-oxide] was analyzed in the presence or absence of P450s. Styrene oxide hydrolysis was activated by all P450s including the CYP1A, 2B, 2C, and 3A subfamilies. In agreement with the association affinity determined by resonant mirror, CYP2C11 tends to have enhanced activity for styrene oxide hydrolysis. On the other hand, B(a)P-oxide hydrolysis was enhanced by only CYP2C11 while CYP1A1 and CYP2B1 had no effect. These results suggest that (1) many P450 enzymes associate nonspecifically with mEH, (2) the CYP2C11 plays a greater role in the association/activation of mEH and (3) the P450-mediated activation of mEH depends upon the substrate of mEH.     

Mitochondrial P450-dependent arachidonic acid metabolism by TCDD-induced hepatic CYP1A5; conversion of EETs to DHETs by mitochondrial soluble epoxide hydrolase

Several P450 enzymes localized in the endoplasmic reticulum and thought to be involved primarily in xenobiotic metabolism, including mouse and rat CYP1A1 and mouse CYP1A2, have also been found to translocate to mitochondria. We report here that the environmental toxin 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) induces enzymatically active CYP1A4/1A5, the avian orthologs of mammalian CYP1A1/1A2, in chick embryo liver mitochondria as well as in microsomes. P450 proteins and activity levels (CYP1A4-dependent 7-ethoxyresorufin-O-deethylase and CYP1A5-dependent arachidonic acid epoxygenation) in mitochondria were 23-40% of those in microsomes. DHET formation by mitochondria was twice that of microsomes and was attributable to a mitochondrial soluble epoxide hydrolase as confirmed by Western blotting with antiEPHX2, conversion by mitochondria of pure 11,12 and 14,15-EET to the corresponding DHETs and inhibition of DHET formation by the soluble epoxide hydrolase inhibitor, 12(-3-adamantan-1-yl-ureido)-dodecanoic acid (AUDA). TCDD also suppressed formation of mitochondrial and microsomal 20-HETE. The findings newly identify mitochondria as a site of P450-dependent arachidonic acid metabolism and as a potential target for TCDD effects. They also demonstrate that mitochondria contain soluble epoxide hydrolase and underscore a role for CYP1A in endobiotic metabolism.     

Forging the links between metabolism and carcinogenesis

Metabolism plays important roles in chemical carcinogenesis, both good and bad. The process of carcinogen metabolism was first recognized in the first half of the twentieth century and developed extensively in the latter half. The activation of chemicals to reactive electrophiles that become covalently bound to DNA and protein was demonstrated by Miller and Miller [Cancer 47 (1981) 2327]. Today many of the DNA adducts formed by chemical carcinogens are known, and extensive information is available about pathways leading to the electrophilic intermediates. Some concepts about the stability and reactivity of electrophiles derived from carcinogens have changed over the years. Early work in the field demonstrated the ability of chemicals to modulate the metabolism of carcinogens, a phenomenon now described as enzyme induction. The cytochrome P450 enzymes play a prominent role in the metabolism of carcinogens, both in bioactivation and detoxication. The conjugating enzymes can also play both beneficial and detrimental roles. As an example of a case in which several enzymes affect the metabolism and carcinogenicity of a chemical, aflatoxin B1 (AFB1) research has revealed insight into the myriad of reaction chemistry that can occur even with a 1s half-life for a reactive electrophile. Further areas of investigation involve the consequences of enzyme variability in humans and include areas such as genomics, epidemiology, and chemoprevention.     

Targeted disruption of the microsomal epoxide hydrolase gene. Microsomal epoxide hydrolase is required for the carcinogenic activity of 7,12-dimethylbenz[a]anthracene.

Microsomal epoxide hydrolase (mEH) is a conserved enzyme that is known to hydrolyze many drugs and carcinogens, and a few endogenous steroids and bile acids. mEH-null mice were produced and found to be fertile and have no phenotypic abnormalities thus indicating that mEH is not critical for reproduction and physiological homeostasis. mEH has also been implicated in participating in the metabolic activation of polycyclic aromatic hydrocarbon carcinogens. Embryonic fibroblast derived from the mEH-null mice were unable to produce the proximate carcinogenic metabolite of 7,12-dimethylbenz[a]anthracene (DMBA), a widely studied experimental prototype for the polycylic aromatic hydrocarbon class of chemical carcinogens. They were also resistant to DMBA-mediated toxicity. Using the two-stage initiation-promotion skin cancer bioassay, the mEH-null mice were found to be highly resistant to DMBA-induced carcinogenesis. In a complete carcinogenesis bioassay, the mEH mice were totally resistant to tumorigenesis. These data establish in an intact animal model that mEH is a key genetic determinant in DMBA carcinogenesis through its role in production of the ultimate carcinogenic metabolite of DMBA, the 3,4-diol-1,2-epoxide.     

Hepatic levels of cytosolic, microsomal and 'mitochondrial' epoxide hydrolases and other drug-metabolizing enzymes after treatment of mice with various xenobiotics and endogenous compounds

This study was performed in order to study the response of epoxide hydrolases in different subcellular compartments of mouse liver to treatment with various compounds. Male C57BL/6 mice were treated with 31 different compounds--including traditional inducers of xenobiotic-metabolizing systems, liver carcinogens, stilbene derivatives, endogenous compounds and various other drugs and xenobiotics. The effects on liver somatic index; protein contents in 'mitochondria', microsomes and cytosol prepared from the liver; epoxide hydrolase activity towards trans- or cis-stilbene oxide in these three fractions; microsomal cytochrome P-450 content; cytosolic and 'mitochondrial' glutathione transferase activity and cytosolic DT-diaphorase activity were then determined. Cytosolic epoxide hydrolase activity was induced by chlorinated paraffins, di(2-ethylhexyl)phthalate and clofibrate and depressed by alpha-naphthylisothiocyanate, 3-methylcholanthrene, benzil and quercitin. Radial immunodiffusion revealed similar changes in the amount of enzyme protein present, except for two cases, where the increase in amount was larger; and the enzyme seems to be inhibited by benzil. Microsomal epoxide hydrolase activity was induced by these same compounds and several others as well, including dibenzoylmethane, butylated hydroxyanisole and polychlorinated biphenyls. 'Mitochondrial' epoxide hydrolase activity towards trans-stilbene oxide was not affected by those compounds which induced the cytosolic enzyme, but increased about two-fold after treatment with 2-acetylaminofluorene, DL-ethionine, aflatoxin B1 and phenobarbital. There does not seem to be any co-regulation of different forms of epoxide hydrolase in mouse liver. In general small effects were observed on liver weight and protein contents in the different subcellular fractions. Polychlorinated biphenyls were the most potent of the 8 compounds which induced cytochrome P-450, while butylated hydroxyanisole induced cytosolic glutathione transferase activity to the highest extent. 'Mitochondrial' glutathione transferase activity was most induced by certain of the stilbene derivatives. The most potent inducers of DT-diaphorase activity were 3-methylcholanthrene, polychlorinated biphenyls and dinitrotoluene.     

Drug-metabolizing enzyme activities in freshly isolated oval cells and in an established oval cell line from carcinogen-fed rats

The activities of several different phase I and phase II drug-metabolizing enzymes were measured in freshly isolated oval cells from rats fed a choline-deficient/DL-ethionine-supplemented diet for 6 weeks and alsoin vitro in the established oval cell line OC/CDE 6. No cytochrome P450 was spectrophotometrically measurable in both preparations and two cytochrome P450-dependent monoxygenase activities, aminopyrineN-demethylase and ethoxyresorufinO-deethylase, could not be detected in the oval cells of both sources. However, cytosolic glutathione transferase, microsomal expoxide hydrolase and UDP-glucuronosyltransferase activities were clearly measurable in oval cells. Similar enzyme activities were found in freshly isolated and cultured oval cells. The highest activities of these three enzymes were detected during the exponential growth phase of the cultured cells; thereafter the activities decreased until the cells reached confluency. Changes in phenol UDP-glucuronosyltransferase (UGT1A1) mRNA levels paralleled the variations in UDP-glucuronosyltransferase activity, i.e. they were high in exponentially growing oval cells and low in confluent cell cultures. Taking into account that oval cells are able to proliferate in the livers of rats continuously fed a choline-deficient/DL-ethionine-supplemented diet and that none of the analyzed drug metabolizing enzymes are involved in the activation or detoxication ofDL-ethionine, the described pattern might be part of a more general, nonspecific, protection mechanism enabling these cells to overcome the cytotoxic effects of a variety of carcinogens and to proliferate even in their presence. Furthermore, the expression of microsomal epoxide hydrolase, cytosolic glutathione transferase and UDP-glucuronosyltransferase appears to depend on the proliferative status of the cells.Abbreviations CDE choline-deficient/DL-ethionine-supplemented diet - GST glutathione transferase - mEH microsomal epoxide hydrolase - UGT UDP-glucuronosyltransferase     

Targeted label-free approach for quantification of epoxide hydrolase and glutathione transferases in microsomes

The aim of this study was to investigate the expression and organ distribution of cytochrome P450 (CYP450) enzymes, microsomal epoxide hydrolase (MEH), and microsomal glutathione-S-transferase (MGST 1, 2, 3) in human liver, lung, intestinal, and kidney microsomes by targeted peptide-based quantification using nano liquid chromatography–tandem multiple reaction monitoring (nano LC-MRM). Applying this method, we analyzed 16 human liver microsomes and pooled lung, kidney, and intestine microsomes. Nine of the CYP450s (CYP1A2, 2B6, 2C8, 2C9, 2C19, 2D6, 2E1, 3A4, 3A5) could be quantified in liver. Except for CYP3A4 and 3A5 existing in intestine, other CYP450s had little content (<0.1 pmol/mg protein) in extrahepatic tissues. MEH and MGSTs could be quantified both in hepatic and in extrahepatic tissues. The highest concentrations of MEH and MGST 1, 2 were found in liver; conversely MGST 3 was abundant in human kidney and intestine compared to liver. The targeted proteomics assay described here can be broadly and efficiently utilized as a tool for investigating the targeted proteins. The method also provides novel CYP450s, MEH, and MGSTs expression data in human hepatic and extrahepatic tissues that will benefit rational approaches to evaluate metabolism in drug development.     

Cytosolic and microsomal epoxide hydrolases are immunologically distinguishable from each other in the rat and mouse

Antibodies raised to homogeneous rat liver microsomal epoxide hydrolase were used to distinguish microsomal epoxide hydrolase from epoxide hydrolase of cytosolic origin in mice and rats. Using double diffusion analysis in agarose gels, we show that anti-rat liver microsomal epoxide hydrolase forms a single precipitin line with solubilized microsomes from rat and mouse liver, but no reaction is seen with the corresponding cytosolic fractions. Rat or mouse microsomal epoxide hydrolase activity (using benzo[a]pyrene 4,5-oxide as substrate) can be completely precipitated out of solubilized preparations by the antibody, which is equipotent against rat and mouse microsomal epoxide hydrolase. No precipitation of cytosolic hydrolase activity (using trans-beta-ethyl styrene oxide as substrate) is seen with any concentration of the antibody tested. Thus, in the case of microsomal epoxide hydrolase, extensive immunological cross-reactivity exists between the two species, rat and mouse. In contrast, no cross-reactivity is detectable between cytosolic and microsomal epoxide hydrolase, even when enzymes from the same species are compared. We conclude that microsomal and cytosolic epoxide hydrolase activities represent distinct and immunologically non-cross-reactive protein species.     

Cytosolic epoxide hydrolase

Epoxide hydrolase activity is recovered in the high-speed supernatant fraction from the liver of all mammals so far examined, including man. For some as yet unexplained reason, the rat has a very low level of this activity, so that cytosolic epoxide hydrolase is generally studied in mice. This enzyme selectively hydrolyzes trans epoxides, thereby complementing the activity of microsomal epoxide hydrolase, for which cis epoxides are better substrates. Cytosolic epoxide hydrolase has been purified to homogeneity from the livers of mice, rabbits and humans. Certain of the physicochemical and enzymatic properties of the mouse enzyme have been thoroughly characterized. Neither the primary amino acid, cDNA nor gene sequences for this protein are yet known, but such characterization is presently in progress. Unlike microsomal epoxide hydrolase and most other enzymes involved in xenobiotic metabolism, cytosolic epoxide hydrolase is not induced by treatment of rodents with substances such as phenobarbital, 2-acetylaminofluorene, trans-stilbene oxide, or butylated hydroxyanisole. The only xenobiotics presently known to induce cytosolic epoxide hydrolase are substances which also cause peroxisome proliferation, e.g., clofibrate, nafenopin and phthalate esters. These and other observations indicate that this enzyme may actually be localized in peroxisomes in vivo and is recovered in the high-speed supernatant because of fragmentation of these fragile organelles during homogenization, i.e., recovery of this enzyme in the cytosolic fraction is an artefact. The functional significance of cytosolic epoxide hydrolase is still largely unknown. In addition to deactivating xenobiotic epoxides to which the organism is exposed directly or which are produced during xenobiotic metabolism, primarily by the cytochrome P-450 system, this enzyme may be involved in cellular defenses against oxidative stress.     

Activation of procarcinogens by human cytochrome P450 enzymes

Enzymatic transformation of most chemical carcinogens is requisite to the formation of electrophiles that cause genotoxicity, and the cytochrome P450 (P450) enzymes are the most prominent enzymes involved in such activation reactions. During the past 15 years the human P450 enzymes have been extensively characterized. Considerable evidence exists that the variation in activity of these enzymes can have important consequences in the actions of drugs. Other studies have been concerned with the activation of procarcinogens by human P450s. Assignments of roles of particular P450s in the metabolism of chemical carcinogens are discussed, along with the current state of evidence for relationships of particular P450s with human cancer.     

Enzymatic Mechanisms Involved in Phenanthrene Degradation by the White Rot Fungus Pleurotus ostreatus

The enzymatic mechanisms involved in the degradation of phenanthrene by the white rot fungus Pleurotus ostreatus were examined. Phase I metabolism (cytochrome P-450 monooxygenase and epoxide hydrolase) and phase II conjugation (glutathione S-transferase, aryl sulfotransferase, UDP-glucuronosyltransferase, and UDP-glucosyltransferase) enzyme activities were determined for mycelial extracts of P. ostreatus. Cytochrome P-450 was detected in both cytosolic and microsomal fractions at 0.16 and 0.38 nmol min(sup-1) mg of protein(sup1), respectively. Both fractions oxidized [9,10-(sup14)C]phenanthrene to phenanthrene trans-9,10-dihydrodiol. The cytochrome P-450 inhibitors 1-aminobenzotriazole (0.1 mM), SKF-525A (proadifen, 0.1 mM), and carbon monoxide inhibited the cytosolic and microsomal P-450s differently. Cytosolic and microsomal epoxide hydrolase activities, with phenanthrene 9,10-oxide as the substrate, were similar, with specific activities of 0.50 and 0.41 nmol min(sup-1) mg of protein(sup-1), respectively. The epoxide hydrolase inhibitor cyclohexene oxide (5 mM) significantly inhibited the formation of phenanthrene trans-9,10-dihydrodiol in both fractions. The phase II enzyme 1-chloro-2,4-dinitrobenzene glutathione S-transferase was detected in the cytosolic fraction (4.16 nmol min(sup-1) mg of protein(sup-1)), whereas aryl adenosine-3(prm1)-phosphate-5(prm1)-phosphosulfate sulfotransferase (aryl PAPS sulfotransferase) UDP-glucuronosyltransferase, and UDP-glucosyltransferase had microsomal activities of 2.14, 4.25, and 4.21 nmol min(sup-1) mg of protein(sup-1), respectively, with low activity in the cytosolic fraction. However, when P. ostreatus culture broth incubated with phenanthrene was screened for phase II metabolites, no sulfate, glutathione, glucoside, or glucuronide conjugates of phenanthrene metabolites were detected. These experiments indicate the involvement of cytochrome P-450 monooxygenase and epoxide hydrolase in the initial phase I oxidation of phenanthrene to form phenanthrene trans-9,10-dihydrodiol. Laccase and manganese-independent peroxidase were not involved in the initial oxidation of phenanthrene. Although P. ostreatus had phase II xenobiotic metabolizing enzymes, conjugation reactions were not important for the elimination of hydroxylated phenanthrene.     

The anti-carcinogenic plant compound indole-3-carbinol differentially modulates P450-mediated steroid hydroxylase activities in mice.

Indole-3-carbinol (I3C), a component of cruciferous vegetables, exhibits anti-carcinogenic activity in a variety of model systems. This activity has been attributed in part to the induction of cytochrome P450 CYP1A subfamily members and the resulting increased metabolic inactivation of chemical carcinogens. The present study was undertaken to assess the effects of I3C on several constitutive P450 activities that contribute to both carcinogen and steroid hormone metabolism. Mice were administered I3C in their diet at estimated daily doses of 250, 500 and 750 mg/kg for 1 week. Liver microsomes from treated and untreated mice were subsequently assayed for CYP1A-mediated ethoxy-resorufin O-deethylase (EROD) activity, estradiol 2-hydroxylase activity and seven different testosterone hydroxylase activities. I3C elevated EROD, estradiol 2-hydroxylase and testosterone 6 alpha-hydroxylase activities in a dose-dependent manner. The other six testosterone hydroxylase activities were not significantly affected by in vivo treatment with I3C. In addition to its effects on steroid hydroxylase activities, I3C also elevated NADPH-cytochrome P450 reductase activity, a necessary component to the P450 monooxygenase system. We next examined the direct in vitro effects of I3C and its acid condensation products, as are generated in the stomach following ingestion, on the P450 catalytic activities. Testosterone 6 beta-hydroxylase, the major testosterone hydroxylase activity in untreated mice, was significantly inhibited (IC50 approximately 12 micrograms/ml) by the acid condensation products of I3C. In contrast, all other P450 activities were not appreciably affected by I3C or its acid condensation products. These results indicate that I3C can elicit both inductive and suppressive effects on the constitutive P450s that participate in carcinogen and steroid hormone metabolism. This pleiotropic effect on hepatic catalytic enzymes may contribute to the anti-carcinogenic properties of this compound.     

Interaction between cytochrome P450 and other drug-metabolizing enzymes: evidence for an association of CYP1A1 with microsomal epoxide hydrolase and UDP-glucuronosyltransferase

Protein-protein interactions between cytochrome P450 (P450) and other drug-metabolizing enzymes were studied by affinity chromatography using CYP1A1-, glycine-, and bovine serum albumin (BSA)-conjugated Sepharose 4B columns. Sodium cholate-solubilized microsomes from phenobarbital-treated rat liver were applied to the columns and the material eluted with buffer containing NaCl was analyzed by immunoblotting. Microsomal epoxide hydrolase (mEH) and UDP-glucuronosyltransferases (UGTs), as well as NADPH-P450 reductase, were efficiently trapped by the CYP1A1 column. Glycine and BSA columns exhibited no ability to retain these proteins. Protein disulfide isomerase and calnexin, non-drug-metabolizing enzymes expressed in the endoplasmic reticulum, were unable to associate with the CYP1A1 column. These results suggest that CYP1A1 interacts with mEH and UGT to facilitate a series of multistep drug metabolic conversions.     

Differential time course of induction of rat liver microsomal cytochrome P-450 isozymes and epoxide hydrolase by Aroclor 1254

The time course of induction of rat liver microsomal cytochromes P-450a, P-450b + P-450e, P-450c, and P-450d and epoxide hydrolase has been determined in immature male rats administered a single large dose [1500 mumol (500 mg)/kg body wt] of the polychlorinated biphenyl mixture Aroclor 1254. Differential regulation of these xenobiotic-metabolizing enzymes was indicated by their characteristic patterns of induction. The rate of induction of cytochrome P-450a and epoxide hydrolase was relatively slow, and steady-state levels of these enzymes were maintained from approximately Days 9 to 15 after Aroclor 1254 treatment. In contrast, cytochrome P-450c was maximally induced 2 days after Aroclor 1254 treatment and remained at a constant level through Day 15. Steady-state levels of cytochrome P-450d, beginning 1 week after Aroclor 1254 treatment, were preceded by a fairly rapid rate of induction and possibly by a small decline from maximal levels observed around Days 4 to 5. Like those of the other cytochrome P-450 isozymes and epoxide hydrolase, the levels of cytochromes P-450b + P-450e were constant from Day 9 to 15 after Aroclor 1254 treatment. However, an unexpected but reproducible decline (approximately 25%) in total cytochrome P-450 content observed between Days 4 and 9 after Aroclor 1254 treatment principally reflected a dramatic and totally unanticipated decrease (approximately 45%) in the level of cytochromes P-450b + P-450e. This transient decline in the level of cytochromes P-450b + P-450e was not due to an unusual effect of a mixture of polychlorinated biphenyls, since identical results were obtained with two individual congeners, namely 2,3,4,5,4'-penta- and 2,3,4,5,3',4'-hexachlorobiphenyl, that induced the same isozymes as Aroclor 1254. In contrast, when rats were treated with 2,4,5,2',4',5'-hexachlorobiphenyl, which induces cytochromes P-450a and P-450b + P-450e and epoxide hydrolase but not cytochromes P-450c or P-450d, maximal levels of cytochromes P-450b + P-450e were attained on Day 4 and no decrease was observed over the next 11 days. These results suggest that there may be an interaction in the regulation of induction of certain individual cytochrome P-450 isozymes.     

Epoxide hydrolases: biochemistry and molecular biology

Epoxides are organic three-membered oxygen compounds that arise from oxidative metabolism of endogenous, as well as xenobiotic compounds via chemical and enzymatic oxidation processes, including the cytochrome P450 monooxygenase system. The resultant epoxides are typically unstable in aqueous environments and chemically reactive. In the case of xenobiotics and certain endogenous substances, epoxide intermediates have been implicated as ultimate mutagenic and carcinogenic initiators Adams et al. (Chem. Biol. Interact. 95 (1995) 57-77) Guengrich (Properties and Metabolic roles 4 (1982) 5-30) Sayer et al. (J. Biol. Chem. 260 (1985) 1630-1640). Therefore, it is of vital importance for the biological organism to regulate levels of these reactive species. The epoxide hydrolases (E.C. 3.3.2. 3) belong to a sub-category of a broad group of hydrolytic enzymes that include esterases, proteases, dehalogenases, and lipases Beetham et al. (DNA Cell Biol. 14 (1995) 61-71). In particular, the epoxide hydrolases are a class of proteins that catalyze the hydration of chemically reactive epoxides to their corresponding dihydrodiol products. Simple epoxides are hydrated to their corresponding vicinal dihydrodiols, and arene oxides to trans-dihydrodiols. In general, this hydration leads to more stable and less reactive intermediates, however exceptions do exist. In mammalian species, there are at least five epoxide hydrolase forms, microsomal cholesterol 5,6-oxide hydrolase, hepoxilin A(3) hydrolase, leukotriene A(4) hydrolase, soluble, and microsomal epoxide hydrolase. Each of these enzymes is distinct chemically and immunologically. Table 1 illustrates some general properties for each of these classes of hydrolases. Fig. 1 provides an overview of selected model substrates for each class of epoxide hydrolase.     

Loss of cytochrome P-450 from hepatic nuclear membranes of rats fed 2-acetylaminofluorene

The cytochrome P-450 content of nuclear membranes isolated from the livers of male Sprague-Dawley rats fed a semipurified diet containing 0.05% w/w 2-acetylaminofluorene (AAF) for 3 weeks, was only about 20% of the values in control rats fed the same diet devoid of AAF. This effect was apparent after only 1 week of AAF treatment and persisted in nuclear membranes from isolated hyperplastic nodules (HPN) generated by 4 cycles of interrupted AAF-feeding. The microsomal cytochrome P-450 content, on the other hand, remained at control levels after 1 week of AAF treatment, and it was only slightly decreased after 3 weeks. In contrast, microsomes from HPN generated by prolonged AAF treatment had markedly decreased amounts of cytochrome P-450. The AAF treatment also caused changes in cholesterol epoxide hydrolase activity, which paralleled those observed for cytochrome P-450 content. Nuclear membranes from livers of rats fed AAF for 3 weeks, and from isolated HPN, had only 30-50% of the cholesterol epoxide hydrolase activity present in controls, whereas the microsomal enzyme activity remained at control levels after 3 weeks of AAF feeding but was 50% depressed in microsomes from HPN. The selective loss of cytochrome P-450 and of cholesterol epoxide hydrolase in hepatic nuclear membrane, but not in microsomes, of rats fed AAF for 3 weeks suggests independent control for these enzymes in these two membrane fractions. Cytochrome P-450 plays a role both in the activation of AAF (N-hydroxylation) as well as in its detoxification (ring hydroxylation) whereas cholesterol epoxide hydrolase initiates the detoxification of cholesterol epoxide. Therefore, our findings suggest the hypothesis that AAF treatment causes an early loss, at the surface of the nucleus, of the last line of defense for detoxification of transforming or promoting metabolites generated by microsomal activation of natural substances such as cholesterol and of xenobiotics such as AAF.     

The effects of metyrapone, chalcone epoxide, benzil, clotrimazole and related compounds on the activity of microsomal epoxide hydrolase in situ, in purified form and in reconstituted systems towards different substrates

The influence of metyrapone, chalcone epoxide, benzil and clotrimazole on the activity of microsomal epoxide hydrolase towards styrene oxide, benzo[a]pyrene 4,5-oxide, estroxide and androstene oxide was investigated. The studies were performed using liver microsomes from rats, rabbits, mice and humans; epoxide hydrolase purified from rat liver microsomes to apparent homogeneity; and the purified enzyme incorporated into liposomes composed of egg-yolk phosphatidylcholine or total rat liver microsomal lipids. All four effectors were found to activate the hydrolysis of styrene oxide by epoxide hydrolase in situ in rat liver microsomal membranes, in agreement with earlier findings. Epoxide hydrolase activity towards styrene oxide in liver microsomes from mouse, rabbit and man was also increased by all four effectors. The most striking effect was a 680% activation by clotrimazole in rat liver microsomes. However, none of the effectors activated microsomal epoxide hydrolase more than 50% when benzo[a]pyrene 4,5-oxide, estroxide or androstene oxide was used as substrate. Indeed, clotrimazole was found to inhibit microsomal epoxide hydrolase activity towards estroxide 30-50% and towards androstene oxide 60-90%. The effects of these four compounds were found to be virtually identical in the preparations from rats, rabbits, mice and humans. The effects of metyrapone, chalcone epoxide, benzil and clotrimazole on purified epoxide hydrolase were qualitatively the same as those on epoxide hydrolase in intact microsomes, but much smaller in magnitude. These effects were increased in magnitude only slightly by incorporation of the purified enzyme into liposomes made from egg-yolk phosphatidylcholine. However, when incorporation into liposomes composed of total microsomal lipids was performed, the effects seen were essentially of the same magnitude as with intact microsomes. When the extent of activation was plotted against effector concentration, three different patterns were found with different effectors. Activation of epoxide hydrolase activity towards styrene oxide by clotrimazole was found to be uncompetitive with the substrate and highly structure specific. On the other hand, inhibition of epoxide hydrolase activity towards androstene oxide by clotrimazole was found to be competitive in microsomes. It is concluded that the marked effects of these four modulators on microsomal epoxide hydrolase activity are due to an interaction with the enzyme protein itself, but that the presence of total microsomal phospholipids allows the maximal expression leading to similar degrees of modulation as those observed in intact microsomes.(ABSTRACT TRUNCATED AT 400 WORDS)     

Role of cytochromes P450 in chemical toxicity and oxidative stress: studies with CYP2E1

Cytochromes P450 are responsible for metabolism of most xenobiotics and are required for the efficient elimination of foreign chemicals from the body. Paradoxically, these enzymes also metabolically activate biologically inert compounds to electrophilic derivatives that can cause toxicity, cell death and sometimes cellular transformation resulting in cancer. To establish the role of these enzymes in toxicity and carcinogenicity in vivo, gene knockout mice have been developed. To illustrate the role of P450s in toxicity, CYP2E1-null mice were employed with the commonly used analgesic drug acetaminophen. CYP2E1 is the rate-limiting enzyme that initiates the cascade of events leading to acetaminophen hepatotoxicity; in the absence of this P450, toxicity will only be apparent at high concentrations. Other enzymes and nuclear receptors are also involved in activation or inactivating chemicals. CYP2E1 is induced by alcohol and the primary P450 that carries out ethanol oxidation that can lead to the production of activated oxygen species and oxidative stress that elevate ERK1/2 phosphorylation through EGRF/c-Raf signaling. Paradoxically, activation of this pathway inhibits apoptotic cell death stimulated by reactive oxygen generating chemicals but accelerates necrotic cell death produced by polyunsaturated fatty acids. CYP2E1 is thought to contribute to liver pathologies that result from alcoholic liver disease and non-alcoholic steatohepatitis.