ACYL CARRIER PROTEIN. 3. AN ENOYL HYDRASE SPECIFIC FOR ACYL CARRIER PROTEIN THIOESTERS.
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In the present paper, a simple photometric assay of microsomal epoxide hydrolase activity using the 4-NBP test is described. The outline of this method is the reaction of 4-NBP with the unreacted oxide extracted from incubation medium in separated ethyl-acetate layer, followed by measurement of absorbancy at 560 nm. The usefulness of this assay can be in application to all epoxides enough alkylating and it can be used for routine analyses which don't request either particular instruments or suitable standards of synthesis.
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With 8-(14)C-styrene oxide as substrate, specific glutathione S-transferase and epoxide hydrase activities were determined in subcellular fractions of liver, lungs, kidney, and intestinal mucosa from rabbit, rat, and guinea pig. Liver had the highest enzyme activities in each species. Rat and guinea pig had higher glutathione S-transferase activity in both liver and kidney than rabbit. Rat testis also had appreciable glutathione S-transferase activity. The perinatal development of epoxide hydrase and glutathione S-transferase was followed in liver and several extrahepatic tissues of fetal and neonatal guinea pigs and rabbits. The rates at which enzyme activities reached adult levels in the extrahepatic tissues differed from the liver in both species. Epoxide hydrase and glutathione S-transferases developed at different rates in each organ, demonstrating that the relative importance of these two detoxifying pathways for styrene oxide may shift before and after birth. The effects of pretreating male and female rats with phenobarbital (PB), 1,2,3,4-dibenzanthracene (DBA), pregnenolone-16alpha-carbonitrile (PCN), or 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on hepatic and extrahepatic epoxide hydrase and glutathione S-transferase activities toward styrene oxide were determined. PB increased both enzyme activities in liver of both sexes. PCN induced only glutathione S-transferase activity in female liver. Extrahepatic epoxide hydrase and glutathione S-transferase activities were unaffected except that TCDD doubled female renal epoxide hydrase activity and PB increased intestinal epoxide hydrase activity in both sexes. Styrene oxide biotransformation was studied in isolated, perfused rat liver and rabbit lung preparations. Conjugation with glutathione was a major metabolic pathway although significant amounts of diol were also formed in each instance. In rat liver, 27-40% of the administered styrene oxide was excreted via the bile mainly as S-(1-phenyl-2-hydroxyethyl)glutathione.
The biochemical properties of preneoplastic antigen (PN antigen) were investigated in order to resolve inconsistencies in previous reports. First of all, epoxide hydrase was purified biochemically from the liver of phenobarbital-treated rats and anti epoxide hydrase serum was prepared in rabbits. Immunochemically, in Ouchterlony double diffusion, PN antigen had the same antigenicity as epoxide hydrase. From an immunoprecipitation study using sodium dodecyl sulfate-polyacrylamide gel electrophoresis and crossed immunoelectrophoresis, it was found that PN antigen may be composed of epoxide hydrase and at least one more protein (mol. wt. 27,000). However, the biochemical and biological properties of the protein binding to epoxide hydrase were not determined. The existence of PN antigen (epoxide hydrase and its binding protein) may be associated with microsomal membrane alterations during chemical carcinogenesis.
A highly purified and reconstituted hepatic microsomal monooxygenase system, completely free of epoxide hydrase and consisting of cytochrome P-448 from 3-methylcholanthrene-treated rats, NADPH-cytochrome c reductase, phosphatidylcholine, and NADPH, metabolizes benzo (a)pyrene to products highly mutagenic in strains TA 98 and TA 1538 of Salmonella typhimurium. The formation of mutagenic metabolites is completely dependent on the presence of benzo (a)pyrene, NADPH, NADPH-cytochrome c reductase, and cytochrome P-448 and is partially dependent on phosphatidylcholine. Mutation frequency in both strains is linearly related to amount of cytochrome P-448 and to time of incubation. Highly purified cytochrome P-450 from phenobarbital-treated rats is relatively poor in catalyzing the formation of mutagenic metabolites from benzo (a)pyrene. Addition of 7.5 to 75 units of highly purified epoxide hydrase to the cytochrome P-448-dependent monooxygenase system decreases the number of mutations by approximately 50% and30% in strains TA 1538 and TA 98, respectively. Additional amounts of epoxide hydrase (300 units) fail to further suppress mutations, indicating that at least some, but probably not all, of the mutagenic metabolites of benzo (a)pyrene are arene oxides. In the absence of a monooxygenase system, mutations induced by benzo (a)pyrene 4,5-oxide are readily quenched by epoxide hydrase, whereas mutations induced by a diol epoxide metabolite of benzo (a)pyrene [(+/-)-7 beta, 8alpha-dihydroxy-9beta, 10beta-epoxy-7,8,9,10-tetrahydrobenzo (a)pyrene] are not. Several known and potential phenolic and dihydrodiol metabolites of benzo (a)pyrene are metabolized to products mutagenic in the Salmonella. The number of mutations induced per nmol of hemoprotein is approximately 3- to 4-fold higher when trans-7,8-dihydroxy-7,8-dihydrobenzo (a)pyrene replaces benzo (a)pyrene as a substrate for the cytochrome P-448-dependent monooxygenase system. Little or no mutagenic activity is observed with trans-dihydrodiols at positions 4,5, 9,10, or 11,12 of the hydrocarbon, either in the absence or presence of the active monooxygenase system. Of the 12 possible isomeric monophenols of benzo (a)-pyrene, only 6- and 12-hydroxybenzo (a)pyrene are moderately active bacterial mutagens; 1-, 2-, 3-, 6-, 9-, and 12-hydroxybenzo (a)pyrene are premutagens (i.e. metabolized to mutagenic products); and 4-, 5-, 7-, 8-, 10-, and 11-hydroxybenzo (a)pyrene have little or no mutagenic activity with or without further oxidative metabolism. Benzo (a)pyrene 7,8-oxide, a carcinogen on mouse skin, is weakly mutagenic but can be further metabolized to a highly active bacterial mutagen(s), presumably diol epoxide(s), by a combination of epoxide hydrase and the cytochrome P-448 monooxygenase system. This is the first example of a direct role of epoxide hydrase in the metabolic activation of a chemical to a toxic product.
The effect of oral administration of the pyrrolizidine alkaloids, seneciphylline and senecionine, from Senecio vulgaris (Compositae) on activities of hepatic epoxide hydrase, glutathione-S-transferase, aminopyrine-N-demethylase and arylhydrocarbon hydroxylase (AHH) was investigated in microsomes of young male albino rats. Seneciphylline significantly increased the activities of epoxide hydrase and glutathione-S-transferase but caused reduction of cytochrome P-450 and related monooxygenase activities. Senecionine failed to stimulate epoxide hydrase while it diminished the activities of glutathione-S-transferase, aminopyrine demethylase and AHH. Seneciphylline and senecionine could not produce any prominent in vitro effect on the hepatic drug metabolizing enzymes under study, except slight stimulation of epoxide hydrase activity by both the alkaloids and slight reduction of aminopyrine demethylase activity by senecionine.
This article reports the effect of coexposure to Indian chrysotile asbestos (5 mg/rat) and kerosene soot (5 mg/rat) on the pulmonary phase I and phase II drug-metabolizing enzymes 1, 4, 8, 16, 30, 90, and 150 days after a single intratracheal inoculation. Exposure to soot resulted in a significant induction of the pulmonary microsomal cytochrome P450 and the activity of dependent monooxygenase, benzo(a)pyrene (B[a]P) hydroxylase, and epoxide hydrase at all time intervals. On the other hand, the cytosolic glutathione S-transferase (GST) activity was induced at days 1, 4, 8, 16, and 30 after exposure, followed by inhibition in the enzyme activity. In contrast, chrysotile exposure depleted cytochrome P450, B[a]P hydroxylase, epoxide hydrase, and GST at initial stages, while all these parameters except GST were induced at later stages. However, coexposure to chrysotile and soot led to a significant inhibition in the cytochrome P450 levels, activities of B[a]P hydroxylase, epoxide hydrase, and GST at initial stages of exposure. At advanced stages, however, an additional increase in cytochrome P450, B[a]P hydroxylase, and epoxide hydrase but a decrease in GST was observed. These results clearly show that the intratracheal coexposure to high levels of asbestos and kerosene soot alters the metabolic activity of the lung, which is turn may retain toxins in the system for a longer period, resulting in adverse pathological disorders.