Microsomal and cytosolic epoxide hydrolase and glutathione S-transferase activities in the gill, liver, and kidney of the rainbow trout, Salmo gairdneri. Baseline levels and optimization of assay conditions

Microsomal and cytosolic epoxide hydrolase (mEH and cEH respectively) and glutathione S-transferase (GST) activities were measured in the liver, kidney, and gills of rainbow trout. Assays were optimized for time, pH, and temperature, using trans-stilbene oxide (TSO) and cis-stilbene oxide (CSO) as substrates for cEH and mEH, respectively. Optimal pH values for mEH, cEH, and GST were similar to mammalian values (i.e. 8.5, 7.5, and 9). Temperature optima differed between tissues and cell fractions. Specific activity of cEH-TSO was 3-14 times greater than mEH-CSO for all three tissues, and 8-60 times greater on a tissue weight basis. Liver and, to a lesser extent, kidney mEH were active against benzo[a]pyrene 4,5-oxide, whereas gill mEH was not active against this substrate. Liver cytosolic GST was active against CSO and 1-chloro-2,4-dinitrobenzene (CDNB) but not TSO, whereas gill and kidney cytosolic GST were active only against CDNB. Liver and kidney microsomal GST were active against CDNB, but no activity was found in gill microsomes. The results are discussed in relation to possible endogenous substrates and uninduced xenobiotic metabolizing capacities of different trout tissues.     

Organ distribution of epoxide hydrolases in cytosolic and microsomal fractions of normal and nafenopin-treated male DBA/2 mice

Using trans-stilbene oxide and styrene oxide as substrates, epoxide hydrolase activities were measured in cytosolic and microsomal fractions from liver, kidney, heart, lung and testis of male DBA/2 mice. The activities towards these two substrates are remarkably organ specific: trans-stilbene oxide was most effectively hydrolyzed in subcellular fractions from liver, kidney and heart, whereas styrene oxide was predominantly hydrolyzed in those from liver, lung and testis. Immunoblotting experiments were performed with two polyclonal antibodies isolated from goat antisera. Using an anti-mouse liver cytosolic epoxide hydrolase antibody, the corresponding antigen protein was predominantly detected in both cytosolic and microsomal fractions from liver, kidney and heart. An anti-rat liver microsomal epoxide hydrolase antibody proved to be cross-reactive with the mouse enzyme and stained SDS-gels run with microsomal fractions from liver, lung and testis. The anti-mouse liver cytosolic epoxide hydrolase antibody precipitated cytosolic epoxide hydrolase activities from liver, kidney and heart cytosolic fractions. Dietary exposure to the hypolipidemic agent nafenopin (2000 ppm/10 days) caused an induction of trans-stilbene oxide hydrolase and styrene oxide hydrolase activities in cytosolic and microsomal liver fractions whereas, in the other organs, the same activities were unaffected by this treatment. This finding was in accordance with the increased amounts of antigen protein as detected with the antibodies in liver fractions from treated animals. The anti-mouse liver cytosolic epoxide hydrolase antibody was found to precipitate the whole trans-stilbene oxide hydrolase activity also from liver cytosol of nafenopin-treated mice, which indicates the presence of a single cytosolic epoxide hydrolase following induction.     

Effect of dietary clofibrate on epoxide hydrolase activity in tissues of mice

The effects of dietary clofibrate on the epoxide-metabolizing enzymes of mouse liver, kidney, lung and testis were evaluated using trans-stilbene oxide as a selective substrate for the cytosolic epoxide hydrolase, cis-stilbene oxide and benzo[a]pyrene 4,5-oxide as substrates for the microsomal form, and cis-stilbene oxide as a substrate for glutathione S-transferase activity. The hydration of trans-stilbene oxide was greatest in liver followed by kidney greater than lung greater than testis. Its hydrolysis was increased significantly in the cytosolic fraction of liver and kidney of clofibrate-treated mice and in the microsomes from the liver. Isoelectric focusing indicates that the same enzyme is responsible for hydrolysis of trans-stilbene oxide in normal and induced liver and kidney. Clofibrate induced glutathione S-transferase activity on cis-stilbene oxide only in the liver. Hydrolysis of both cis-stilbene oxide and benzo[a]pyrene 4,5-oxide was highest in testis followed by liver greater than lung greater than kidney. Hydration of cis-stilbene oxide was induced significantly in both liver and kidney by clofibrate but that of benzo[a]pyrene 4,5-oxide was induced only in the liver. These and other data based on ratios of hydration of benzo[a]pyrene 4,5-oxide to cis-stilbene oxide in tissues of normal and induced animals indicate that there are one or more novel epoxide hydrolase activities which cannot be accounted for by either the classical cytosolic or microsomal hydrolases. These effects are notable in the microsomes of kidney and especially in the cytosol of testis.     

Hepatic epoxide hydrolase activities and their induction by clofibrate and diethylhexylphthalate in various strains of mice

The presence of epoxide hydrolase activity in cytoplasm, microsomes and mitochondrial fraction in livers from twelve strains of mice (AKR/J, A/J, BALB/cByJ, CBA/J, C3H/HeJ, G57BL/6J, C57BL/10J, DBA/2J, NZB/B1NJ, PL/J, SEC/1ReJ and SW), and the influence of orally administered clofibrate and di(2-ethylhexyl)phthalate (DEHP) (0.5 and 2%, respectively, in diet) on epoxide hydrolase activities, were studied. Significant differences in basal cytosolic epoxide hydrolase activity, which ranged from 5.6 to 11.2 nmol diol.min-1.(mg protein)-1 using trans-stilbene oxide (TSO) as substrate, were noted among the mice. The highest and lowest enzyme levels were observed in the A/J and DBA/2J strains respectively. Similarly, microsomal epoxide hydrolase activity, monitored with cis-stilbene oxide (CSO), varied with the mouse strain, with the highest and lowest microsomal epoxide hydrolase activity being observed in A/J and SW strains respectively. Variations were also noted in the epoxide hydrolase activity in the mitochondrial fraction (monitored with TSO) with the highest and lowest levels observed in C57BL/6J and SW strains respectively. Clofibrate or DEHP treatment induced both cytosolic and microsomal epoxide hydrolases in nearly all of the strains examined. In contrast, the hydrolysis of TSO by the mitochondrial fraction in these strains was either not affected or decreased by clofibrate or DEHP treatment. The induction of cytosolic epoxide hydrolase was found to range between 1.2- and 2.8-fold, with generally a higher level of induction in mouse strains with low basal levels of cytosolic epoxide hydrolase activity. This level of cytosolic epoxide hydrolase activity, monitored with TSO as substrate, closely reflected the level of cytosolic epoxide hydrolase protein detected by immunoblot. There were also no significant differences observed in the molecular weight, immunological characteristics, pH-dependence and heat stability of hepatic cytosolic epoxide hydrolase activities of control and clofibrate-treated mice from various strains. These results suggest that clofibrate and DEHP induce both cytosolic and microsomal epoxide hydrolases but not the epoxide hydrolase in the mitochondrial fraction.     

Induction of epoxide hydrolase in cultured rat hepatocytes and hepatoma cell lines

The expression of epoxide hydrolases was studied in cultured rat hepatocytes and hepatoma cell lines. Styrene 7,8-oxide and benzo[a]pyrene 4,5-oxide were used as substrates for microsomal epoxide hydrolase and trans-stilbene oxide for the cytosolic form of this enzyme. In freshly isolated hepatocytes from control rats, microsomal epoxide hydrolase activity was 7.7 and 10.8 nmoles/mg cellular protein/min with benzo[a]pyrene 4,5-oxide and styrene 7,8-oxide as substrates respectively. This enzyme activity increased by more than 2-fold in hepatocytes after 24 hr in culture and remained elevated throughout 96 hr using both substrates. In cultured hepatocytes from rats pretreated in vivo with phenobarbital, trans-stilbene oxide, 2-acetylaminofluorene and N-hydroxy-2-acetylaminofluorene, both benzo[a]pyrene 4,5-oxide and styrene 7,8-oxide hydrolase activities were increased greater than 1.8 relative to controls. Hepatocytes from 2-acetylaminofluorene-pretreated animals at 24 hr in culture had approximately 9-fold higher activities than control hepatocytes. In marked contrast to microsomal epoxide hydrolase activity, the cytosolic enzyme showed an initial activity of 191 pmoles/mg cellular protein/min in freshly isolated hepatocytes, decreased by 75% after 24 hr in culture, and was barely detectable at 96 hr. A similar trend was apparent in hepatocytes from the pretreated animals. In vitro treatment of hepatocytes with trans-stilbene oxide and phenobarbital increased microsomal epoxide hydrolase, while this activity was refractory to 2-acetylaminofluorene treatment. Styrene 7,8-oxide hydrolase activity was increased in the McA-RH-7777 rat hepatoma cell line by phenobarbital, trans-stilbene oxide and 2-acetylaminofluorene treatment. Similarly, benzo[a]pyrene 4,5-oxide hydrolase activity was also increased in this cell line by treatment with phenobarbital and trans-stilbene oxide but not by 2-acetylaminofluorene. Microsomal epoxide hydrolase activity in rat H4-II-E hepatoma cells was refractory to induction, except by trans-stilbene oxide treatment, which caused a 70% increase in benzo[a]pyrene 4,5-oxide hydrolase activity.     

Effects of environmentally encountered epoxides on mouse liver epoxide-metabolizing enzymes

Male mice were treated (i.p.) for 3 days with 15 different environmentally encountered epoxides, and the effects of these compounds on liver microsomal and cytosolic epoxide hydrolase (mEH and cEH), glutathione S-transferase (mGST and cGST) and carboxylesterase (mCE) activities were determined. The epoxides included the pesticides: heptachlor epoxide, dieldrin, tridiphane, and juvenoid R-20458; the natural products: disparlure, limonin, nomilin, and epoxymethyloleate; the endogenous steroids: lanosterol epoxide, cholesterol-alpha-epoxide, and progesterone epoxide; and the industrial or synthetic epoxides: epichlorohydrin, araldite, trans-stilbene oxide, and 4'-phenylchalcone oxide. The pesticide epoxides were the most effective inducers of liver weight, microsomal protein, and the enzyme activities measured, with mEH and cEH activities towards cis-stilbene oxide (mEHcso and cEHcso), cGST activities towards four of five substrates, and mCE towards clofibrate (mCEclof) and p-nitrophenylacetate (mCEpna) increased following treatment with most of the pesticides. The synthetic epoxides increased some of the same activities, while the natural products, except for increases in cGST activities, and endogenous steroid epoxides were generally not inductive. cEH activity towards trans-stilbene oxide (cEHtso) was increased only following treatment with the peroxisome proliferator, tridiphane, but decreased following treatment with several of the epoxides, while microsomal cholesterol epoxide hydrolase (mEHchol) was increased only moderately by disparlure. Microsomes could effectively conjugate glutathione to chlorodinitrobenzene (mGSTcdnb) and cis-stilbene oxide (mGSTcso). These two activities were differentially induced by a few of the epoxides, suggesting that they may be selective substrates for different isozymes of mGST. Correlation coefficients were determined for the relative response of liver weight, subfraction protein, and enzyme activities. A relatively high correlation was found between the response of liver weight and cytosolic hydrolysis of trans-stilbene oxide (r = 0.73) and cis-stilbene oxide (r = 0.62), and cytosolic glutathione conjugation of dichloronitrobenzene (r = 0.66) and trans-stilbene oxide (r = 0.75). In addition, relatively high correlations were found between the different cGST activities, in particular for dichloronitrobenzene with trans-stilbene oxide (r = 0.89). These studies show that there exists a wide variation in the response of xenobiotic-metabolizing enzymes to environmentally encountered epoxides and that a fairly strong correlation exists between the increases in liver size and increases in certain cytosolic enzyme activities; they also suggest further studies concerning the possibility of an additional isozyme of mGST.     

Characterization of multiple epoxide hydrolase activities in mouse liver nuclear envelope

A nuclear envelope-associated epoxide hydrolase in mouse liver that hydrates trans-stilbene oxide has been identified and characterized. This epoxide hydrolase is distinct from the enzyme in nuclear envelopes that hydrates benzo[a]pyrene 4,5-oxide and other arene oxides. This distinction was demonstrated by the criteria of pH optima, response to specific inhibitors in vitro, and precipitation by specific antibodies. The new epoxide hydrolase had a pH optimum of 6.8, was poorly inhibited by trichloropropene oxide, was potently inhibited by 4-phenylchalcone oxide, and did not bind to antiserum against benzo[a]pyrene 4,5-oxide hydrolase. This nuclear enzyme is similar in many of its properties to cytosolic and microsomal trans-stilbene oxide hydrolases and may be nuclear envelope-bound form of these other epoxide hydrolases. It differed from these other trans-stilbene oxide hydrolases in that its affinities for both trans-stilbene oxide (measured as apparent Km) and 4-phenylchalcone oxide (measured as I50) were 4- to 20-fold lower than those of either the cytosolic or microsomal forms.     

Selective inhibition and selective induction of multiple microsomal epoxide hydrolases

The inhibition in vitro and induction in vivo of microsomal trans-stilbene oxide hydrolase have been studied. This microsomal epoxide hydrolase activity is distinguishable from the previously well-defined microsomal arene oxide hydrolase by a number of catalytic criteria. Two substituted chalcone oxides, 4-phenylchalcone oxide and 4'-phenylchalcone oxide, are potent inhibitors of microsomal trans-stilbene oxide hydrolase, but have no apparent activity against benzo[a]pyrene 4,5-oxide hydrolase. Conversely, compounds that are potent inhibitors of benzo[a]pyrene 4,5-oxide hydrolase, including styrene oxide, cyclohexene oxide, and trichloropropene oxide, inhibit microsomal trans-stilbene oxide hydrolase only at very high (millimolar) concentrations. The chalcone oxides inhibit microsomal trans-stilbene oxide hydrolase noncompetitively, and have micromolar or nanomolar affinity constants for the enzyme. Attempts were made to induce microsomal trans-stilbene oxide hydrolase in vivo. Compounds that induced microsomal benzo[a]pyrene 4,5-oxide hydrolase levels in mice did not simultaneously induce trans-stilbene oxide hydrolase levels. Clofibrate was an exception; it induced levels of both enzymes to a small but statistically significant degree. The two microsomal hydrolase activities have, therefore, very different catalytic sites and appear to be under separate genetic control. 4-Phenylchalcone oxide and 4'-phenylchalcone oxide are selective inhibitors of microsomal trans-stilbene oxide hydrolase and may prove to be very useful in assessing the involvement of this enzyme in the metabolism of endogenous or xenobiotic epoxides.     

Microsomal epoxide hydrolase in different rat strains

Epoxide hydrolase activity was determined in hepatic microsomes of adult males of 22 rat strains. The specific activity varied between 4.3 and 12.7 nmole styrene glycol/mg protein per min. The enzyme in F344, DA and Sprague--Dawley rats, strains with low, high and intermediate activity, respectively, was studied in more detail. No differences in substrate specificity and pH-dependence of the activity were observed between the strains with high and low activity, and immunoprecipitation by antibodies raised against microsomal epoxide hydrolase purified from Sprague--Dawley rats showed that the amounts of enzyme protein in microsomes from DA and F344 rats correlated with the activities. These results indicate quantitative rather than qualitative differences in epoxide hydrolase. The enzyme activity was inherited in an autosomal and codominant manner. The hepatic activity in females (about 78% of that in males) and, with the limitation that only few situations were studied, the trans-stilbene oxide-induced activity were under the same genetic control as the basal hepatic activity in males. In contrast, some extrahepatic tissues showed strain differences in epoxide hydrolase activity which contrasted with those found in liver. Hence, the enzyme activity in one tissue cannot serve as a reliable guide to the relative activity in another tissue, unless a specific correlation between the two tissues has been established. Although the strain differences in activity were not very large in themselves, in combination with inter-individual variation, sex differences and effects of the enzyme inducer transstilbene oxide they led to a 20-fold variation in hepatic epoxide hydrolase activity among the rats investigated in the present study.     

Cytosolic epoxide hydrolase in humans: development and tissue distribution

Cytosolic epoxide hydrolase activity was measured towards trans-stilbene oxide in 41 human adult livers, in 40 fetal livers, in 17 placentas and in fetal and adult lungs, kidneys and gut. The cytosolic epoxide hydrolase activity was measurable in all specimens investigated. The rate of formation of trans-stilbene glycol (pmol/min per mg protein, mean±SD) was 55.2±89.6 (fetal liver). 303.2±73.2 (adult liver) and 18.8±13.1 (placenta) In the fetal extrahepatic tissues, the cytosolic epoxide hydrolase activity was 70.0±9.4 (adrenals), 47.6±7.2 (gut), 69.4±22.5 (kidneys) and 43.2±19.2 (lungs) pmol/min per mg protein, whereas in the adult tissues it was 131.2±63.1 (kidneys), 27.8±20.3 (intestine), 8.5±2.8 (lungs) and 7.2±4.2 (urinary bladder) pmol/min per mg protein.     

Studies on the developmental and adrenal regulation of cytosolic and microsomal epoxide hydrolase activities in rat liver.

The present study was undertaken to ascertain developmental profiles of microsomal epoxide hydrolase (mEH) and cytosolic epoxide hydrolase (cEH) enzyme activities in rat liver. During development, mEH activity reached an optimum by 6 weeks of age (63 nmol/min/mg protein). Activities decreased thereafter in both sexes although in adult male liver the activity was twice that measured in adult female liver. Thus, the importance of pituitary maturation was suggested from these findings. Since glucocorticoids have been implicated in the regulation of mEH gene expression the effect of adrenalectomy on mEH activity was investigated in adult male rat liver. The procedure increased mEH activity almost two-fold and the increase was reversed by dexamethasone, but not deoxycorticosterone, administration. With respect to hepatic cEH activity, the developmental profiles indicated that enzyme activity was greatest in rats at 1 week of age (12-15 nmol/min/mg protein) and very little activity was detected beyond 4 weeks of age (approximately 5 nmol/min/mg protein); sex differences in cEH activity were not apparent at any age. Thus, the pituitary appears to be important in the developmental induction of mEH but not cEH. Glucocorticoids appear to provide the major hormonal influence on mEH expression. Thus, the hypothalamus-pituitary-adrenal axis is involved in the regulation of mEH but the regulation of the cEH enzyme remains unclear.     

Epoxide metabolism in the liver of mice treated with clofibrate (ethyl-alpha-(p-chlorophenoxyisobutyrate], a peroxisome proliferator

An increase in cytosolic epoxide hydrolase (cEH) activity occurs in the livers of mice treated with peroxisome proliferating-hypolipidemic-nongenotoxic carcinogens. As increases in activity of epoxide metabolizing enzymes may reflect the carcinogenic mechanism, a detailed comparison of the response of cEH, microsomal epoxide hydrolase (mEH), and cytosolic glutathione S-transferase (cGST) activities using the geometrical isomers trans- and cis-stilbene oxide as substrates has been performed in livers from mice treated with clofibrate (ethyl-alpha-(p-chlorophenoxyisobutyrate]. The maximal increase of cEH activity occurred at lower dietary doses of clofibrate (0.5%) and within a shorter time (5 days) than mEH and cGST (2%, 14 days) activity. After 14 days at 0.5% clofibrate, cEH, mEH, and cGST activities were 250, 175, and 165% and 290, 220, and 75% of control values in male and female mice, respectively. Withdrawal of clofibrate from the diet resulted in a reversion of activities to control values within 7 days. Clofibrate treatment shifted the apparent subcellular compartmentation of all three enzymatic activities with an increase in the ratio of soluble to particulate activity. In particular, the relative specific activity of all three enzymes decreased in the light mitochondrial (peroxisomal) cell fraction, and an increase of a mEH-like activity (benzo[a]pyrene-4,5-oxide and cis-stilbene oxide hydrolysis) in the cytosol occurred. Both the increase of cEH activity and the appearance of mEH-like activity in the cytosol are novel responses of epoxide metabolizing enzymes, which may be related to the novel cellular responses that follow clofibrate treatment, peroxisome proliferation, hypolipidemia, and nongenotoxic carcinogenesis.     

Effect of aging on testicular epoxide hydrolase and glutathione-S-transferase activities in mice

The effect of aging on epoxide hydrolase (EH) and glutathion-S-transferase (GST) activities was investigated in testes of C57BL/6 mice 1-30 months of age. Microsomal EH (mEH) activity, as monitored with cis-stilbene oxide (CSO), showed statistically insignificant changes throughout the lifespan of mice. Although cytosolic EH (cEH) was detected in testes by immunoblotting, the enzyme activity towards trans-stilbene oxide (TSO) could not be measured under the experimental conditions used. Gonadal GST monitored with 1-chloro-2,4-dinitrobenzene (CDNB) as substrate displayed an increasing trend until the mice reached senescence, showing a 3.7-fold increase in the enzyme activity in old animals (30 months) when compared with that in young animals (2 months). However, with CSO as substrate, GST showed no change in activity in mice of different ages.     

Distribution and nature of epoxide hydrolase activity in subcellular organelles of mouse liver

Mouse liver light and heavy mitochondrial fractions contain significant epoxide hydrolase activity in addition to that present in the cytosol and microsomes. As the mitochondrial fraction itself contains a number of subfractions, experiments were designed to determine the localization of the epoxide hydrolase activity in these subfractions. Subcellular fractions were prepared using livers from 6- to 8-week-old Swiss-Webster male mice. Using trans-stilbene oxide (TSO) as substrate, the highest activity was localized in the cytosolic fraction, followed by the light mitochondrial fraction. Subfractionation of the light mitochondrial fraction by isopycnic sucrose density gradient resulted in the separation of mitochondria from peroxisomes as monitored by marker enzymes. The separation of these two subcellular organelles was also confirmed by the electron microscopic studies. Distribution of TSO-hydrolase activity in the sucrose density gradient fractions closely resembled the activity distribution of the peroxisomal markers catalase and urate oxidase, but significant activity was also found in mitochondria. Treatment of mice with clofibrate selectively induced TSO-hydrolase in the cytosol without affecting this enzyme activity in the peroxisomal fraction. There was no difference in the distribution pattern of TSO-hydrolase and marker enzymes in sucrose density gradients of mitochondrial fractions from clofibrate-treated and control mice. The epoxide hydrolase activity in the peroxisomes is immunologically similar to, and also has the same molecular weight as, the cytosolic epoxide hydrolase.     

Concomitant induction of cytosolic but not microsomal epoxide hydrolase with peroxisomal beta-oxidation by various hypolipidemic compounds

The effects of two cholesterol-lowering (probucol and 1-benzyl-imidazole), three triglyceride- and cholesterol-lowering (clofibrate, tiadenol and fenofibrate) and one triglyceride-lowering (acetylsalicylic acid) compounds on the specific activities of two lipid-metabolizing enzymes (cyanide-insensitive peroxisomal beta-oxidation and palmitoyl-CoA hydrolase) and two xenobiotic metabolizing enzymes (cytosolic (cEH) and microsomal epoxide hydrolase (mEHb] from the livers of male Fischer F-344 rats were investigated. With the exception of probucol and acetylsalicylic acid, all compounds tested caused a dose-dependent hepatomegaly. Taken on a weight basis fenofibrate was the most effective inducer, causing a 20-fold induction of peroxisomal beta-oxidation, a 13-fold induction of cEH activity and a 16-fold induction of palmitoyl-CoA hydrolase activity. The other compounds with triglyceride-lowering activity also induced cEH as well as peroxisomal beta-oxidation and palmitoyl-CoA hydrolase activity. The potency of each individual drug was similar for induction of cEH activity as compared with that of peroxisomal beta-oxidation and palmitoyl-CoA hydrolase activity, but very dissimilar for mEHb, which upon treatment with any of the triglyceride-lowering compounds was either not or only minimally (less than 1.5-fold) induced. 1-Benzylimidazole possessing exclusively cholesterol-lowering activity increased mEHb much more than either cEH or peroxisomal beta-oxidation. The absence of an enhancement of cEH activity in in vitro studies confirmed that the increase in enzyme activity by the test compounds is not caused by activation. cEH activity was also induced in the kidney but only about 2-fold by fenofibrate, tiadenol and acetylsalicylic acid.(ABSTRACT TRUNCATED AT 250 WORDS)     

Species and organ specificity of the trans-stilbene oxide induced effects on epoxide hydratase and benzo(a)pyrene monooxygenase activity in rodents.

It was investigated, whether the selective induction of epoxide hydratase by trans-stilbene oxide (TSO) represents a general phenomenon or is confined to the liver of male rats where it was discovered. Therefore the effect of treatment with TSO on epoxide hydratase and benzo(a)pyrene mono-oxygenase activities were investigated in other organs (kidney, lung, skin, testis), other species (mice, hamsters) and also in female rats. In female rat livers the effect of TSO on the measured enzyme activities was very similar to that found in the male rat liver, i.e. a large induction of epoxide hydratase activity to 300–400 per cent of controls without affecting the benzo(a)pyrene monooxygenase activity. The potency of TSO to induce liver epoxide hydratase activity expressed as per cent of controls was 350:180:140 in rat, mouse and hamster, respectively. Selective induction of epoxide hydratase was found in rat and hamster liver, but not in the mouse liver, where benzo(a)pyrene monooxygenase activity was induced to about the same extent as the epoxide hydratase activity. The only extrahepatie organ in which an increased epoxide hydratase activity was found after TSO treatment was the rat kidney. Subcutaneous and topical treatment with TSO for 12 and 10 days respectively did not induce rat skin epoxide hydratase activity, instead a decrease of the enzyme activity to about 70 per cent ofthat found in control animals was found. Thus, TSO which was demonstrated to be a selective inducer of epoxide hydratase in rat liver can be utilized so far only in a limited number of carcinogenicity test systems, since it failed to induce the skin epoxide hydratase activity, which would have been an excellent tool to study directly the role of epoxide hydratase in the mechanism of skin tumor formation caused by polycyclic hydrocarbons. Interestingly, the epoxide hydratase of the hamster, investigated for the first time in this study, proved quite different from that of rat and mouse in that it hydrated styrene oxide remarkably faster than benzo(a)pyrene 4,5-oxide. This was true for all organs investigated. Also, the organ distribution of epoxide hydratase proved to be very different from that in rat and mouse. In the mouse the activity (with benzo(a)pyrene 4,5-oxide as substrate) was amongst all organs investigated highest in the testis (2.5 fold as compared to liver) but in the hamster the activity was more than 100 fold lower in testis as compared to liver. On the other hand, the activity in kidney was about 50 fold higher in hamster as compared to mouse.     

Subcellular localization of epoxide hydrolase in mouse liver and kidney

The subcellular distribution of epoxide hydrolase activity towards TSO and HEOM in mouse liver and kidney was investigated using zonal rotor centrifugation. Epoxide hydrolase activity towards TSO was found predominantly in the soluble fraction with peroxisomes accounting for activity in the particulate fractions. Renal particulate activity towards HEOM was found predominantly in the microsomes.     

Characterization of distinct forms of cytochromes P-450, epoxide metabolizing enzymes and UDP-glucuronosyltransferases in rat skin

Study of drug metabolizing enzyme activity was undertaken in skin microsomal and cytosolic fractions of male and female rats. The presence of several isoforms was revealed from their activities towards selected substrates and from their cross immunoreactivity using antibodies raised against purified hepatic or renal cytochromes P-450, epoxide hydrolase and UDP-glucuronosyltransferases. Cytochrome P-450 content was precisely quantified by second derivative spectrophotometry, 23.1 and 16.5 pmol/mg protein in males and females, respectively. The monooxygenase activity associated to cytochromes P-450IIB1 and P-450IA1 was determined through O-dealkylation of ethoxy-; pentoxy- and benzoxyresorufin. The activity ranged between 4 and 2 nmol/min/mg protein for male and female rats, respectively. These results and Western blot analysis indicated that rat skin microsomes contain both monooxygenase systems associated with cytochromes P-450IIB1 and P-450IA1. By contrast lauric acid hydroxylation, supported by cytochrome P-450IVA1, was not detectable. Activities of epoxide metabolizing enzymes (microsomal and cytosolic epoxide hydrolases; glutathione S-transferase) were also characterized in skin. Microsomes catalysed the hydratation of benzo(a)pyrene-4,5-oxide and cis-stilbene oxide at the same extent, whatever the sex, although the specific activity was 10 times lower than in liver. The hydratation of trans-stilbene oxide by soluble epoxide hydrolase was four times lower than in the liver. Conjugation of cis-stilbene oxide with glutathione in skin and liver proceeded at essentially similar rates, as the specific activity of glutathione S-transferase in skin was only two times less than that measured in hepatic cytosol. Glucuronidation of 1-naphthol, bilirubin but not of testosterone could be followed in the microsomal fraction. Revelation by Western blot indicated that both the isoforms involved in conjugation of phenols and bilirubin were present in skin microsomes. By contrast, the isoform catalysing the conjugation of testosterone was apparently missing. When immunoblotting was carried out using specific antibodies raised against the renal isoforms, the same result was obtained. In addition, an intense staining corresponding to a 57 kD-protein was observed.     

Comparative induction of drug-metabolizing enzymes by hypolipidaemic compounds

1. The inducing effect of hypolipidaemic compounds containing arylcarboxylic structure (fenofibrate, bezafibrate, ciprofibrate) on drug-metabolizing enzymes was compared with that of other chemically different molecules (probucol, 1-benzylimidazole) in rat liver. 2. Hepatomegaly was closely associated to the decrease in triglycerides and cholesterol contents in plasma. 3. Lauric acid hydroxylation and hydratation of trans-stilbene oxide by the cytosolic epoxide hydrolase were markedly increased by the arylcarboxylic acids (fenofibrate, bezafibrate and ciprofibrate). The determination of the concentration in microsomal epoxide hydrolase by immunoassay revealed no change in the protein amount within the membrane; only the specific activity was enhanced by bezafibrate and 1-benzylimidazole, suggesting an activation process. 4. Bilirubin glucuronidation was increased by the arylcarboxylic structures and by 1-benzylimidazole; by contrast probucol decreased this activity.     

Cigarette smoke inhibits cytosolic but not microsomal epoxide hydrolase of human lung.

The effect of cigarette smoke exposure on the activity of cytosolic and microsomal epoxide hydrolase (EH) has been investigated in human lung. Patients were classified as 'recent smokers' (n = 9) or 'non-recent smokers' (n = 10) according to whether they were or were not still smoking 1 month before surgery. Cytosolic EH was measured with [3H]trans-stilbene oxide as a substrate, whereas microsomal EH was measured with [7-3H]styrene oxide as a substrate. Microsomal EH activity did not differ between recent smokers (2.51 +/- 0.93 nmol min-1 mg-1) and non-recent smokers (2.74 +/- 1.10 nmol min-1 mg-1), whereas cytosolic EH activity was significantly lower in recent smokers (6.46 +/- 1.79 pmol min-1 mg-1) than in non-recent smokers (8.41 +/- 2.09 pmol min-1 mg-1, P less than 0.05). Cytosolic EH activity was correlated with the number of days that had passed since the cessation of smoking (r = 0.58, P less than 0.05) and the effect was dose-dependent, since the enzyme activity was inversely correlated with the number of cigarettes smoked per day (r = 0.85, P less than 0.01). This suggests that recent smoking exposure inhibits the activity of cytosolic EH but not microsomal EH, and that the inhibition increases with the number of cigarettes smoked per day. The contribution of cytosolic enzymes to xenobiotic metabolism may be remarkable in extrahepatic tissues. The inhibition of cytosolic EH by tobacco smoke may reduce the inactivation of carcinogenic epoxides in human lung tissues and so may increase a person's susceptibility to lung cancer.