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Studies on Bacillus stearothermophilus. Part III. Transformation of testosterone.

Bacillus stearothermophilus, a thermophilic bacterium isolated from the Kuwaiti desert, produced a variety of monohydroxy androstene derivatives and an oxidized product when incubated with exogenous testosterone for 24 h at 65 degrees C. The major metabolite was identified as androst-4-en-3,17-dione while minor metabolites included 6 alpha-hydroxyandrost-4-en-3,17-dione, 6 beta-hydroxyandrost-4-en-3,17-dione, 6 alpha-hydroxytestosterone, and 6 beta-hydroxytestosterone. These metabolites were purified by TLC and HPLC followed by their identification using (1)H- and (13)C-NMR and other spectroscopic data.

Biotransformation↗

In vitro bioconversion of [14C]androstenedione by testes of the Siamese fighting fish Betta splendens Regan (Anabantoidei, Belontiidae).

Minced testes of the Siamese fighting fish Betta splendens were incubated with [14C]androstenedione at 27 degrees C for 15, 30, 60, and 120 min. The metabolic products were characterized by paper and thin-layer chromatography, derivative formation, and eventually by crystallization to constant specific activity. After 2 hr of incubation 80.5% of total radioactivity was converted to 11-oxygenated androgens. 11-Ketotestosterone was the main metabolite (56.2%). Our data suggest the existence of two biosynthetic pathways for the formation of 11-ketotestosterone from androstenedione. The sequence androstenedione----testosterone----11 beta-hydroxytestosterone----11-ketotestosterone predominates. To a lesser extent 11 beta-hydroxylation takes place as the first step--followed by formation of 11 beta-hydroxytestosterone and its subsequent oxidation to 11-ketotestosterone.

Androstenedione↗

The biosynthesis of 11-ketotestosterone by the testis of the Siamese fighting fish Betta splendens Regan (Anabantoidei, Belontiidae).

Testicular tissues of the Siamese fighting fish were incubated with [14C]pregnenolone for 10, 20, 30, 50, 80, and 120 min, and with [14C]progesterone, [14C]11 beta-hydroxyandrostenedione, [14C]11 beta-hydroxytestosterone, and [14C]androstenetrione for 120 min. 11-Ketotestosterone was the main metabolite in all 120-min incubations. No 11-oxygenated C21 steroids were found as metabolites of either pregnenolone or progesterone. The biosynthesis of 11-ketotestosterone proceeded through both the delta 5- and the delta 4- pathways as judged from the shape of the yield-time curves of the metabolites of pregnenolone. 11-Ketotestosterone formation from 11-oxygenated precursors increased in the order 11 beta-hydroxytestosterone less than 11 beta-hydroxyandrostenedione less than androstenetrione.

Androstenedione↗

Naringin and naringenin are not the primary CYP3A inhibitors in grapefruit juice.

The effect of various citrus juices and solutions of naringin on CYP3A activity in rat liver microsomes was compared by measuring the formation of 6 beta-hydroxytestosterone from testosterone. Control enzyme activity was reduced by more than 70% by grapefruit juice. Freshly-squeezed sour (Seville) orange juice containing 20% as much naringin was comparable to grapefruit juice in its ability to inhibit microsomal activity. An aqueous solution of naringin at the same concentration as in grapefruit juice produced only a small decrease in 6 beta-hydroxytestosterone formation. Dilution of grapefruit juice with a naringin solution reduced the inhibitory activity of the juice even though naringin concentration did not change. Naringenin did not form under the incubation conditions used indicating that it did not contribute to the inhibition produced by grapefruit juice. Finally, organic extracts of grapefruit juice possessed considerable inhibitory activity even though naringin was not extractable. These data suggest that grapefruit juice inhibits CYP3A activity in vitro and that neither naringin nor naringenin are primarily responsible for this effect. A compound present in both grapefruit juice and Seville orange juice and extractable into organic solvents appears to be responsible.

Animals↗

Improved synthesis of 16alpha-hydroxylated androgens: intermediates of estriol formation in pregnancy.

16alpha-Hydroxyandrostenedione (16alpha-hydroxyandrost-4-ene-3,17-dione), 16alpha-hydroxytestosterone (16alpha,17beta-dihydroxyandrost-4-en-3-one) and 16alpha-hydroxydehydroepiandrosterone 3-sulfate (3beta, 16alpha-dihydroxyandrost-5-en-17-one 3-monosulfate) were synthesized by a new chemical approach with much improved yield. 16alpha-Bromoandrostendione was converted to the hydrazone of 16alpha-hydroxyandrostenedione which gave 16alpha-hydroxyandrostenedione on acid hydrolysis in total 63% yield. Oxidation of 16alpha-hydroxydehydroepiandrosterone with Jones' reagent also selectively afforded 16alpha-hydroxyandrostenedione. 16alpha-Hydroxytestosterone was observed by selective reduction of 16alpha-hydroxyandrostenedione with sodium borohydride. Reaction of 16alpha-hydroxydehydroepiandrosterone with chlorosulfonic acid in pyridine selectively gave the 3-monosulfate. The structure of the sulfate was deduced from its solvolysis to the starting material, and its acetylation and subsequent solvolysis to 16alpha-hydroxydehydroepiandrosterone 16-acetate. All procedures are suitable for large scale synthesis without the use of microorganisms.

Androgens↗

Influence of different combinations of antibodies and penicillinase-labeled testosterone derivatives on sensitivity and specificity of immunoassays.

Three antisera raised against bovine serum albumin (BSA) conjugates of testosterone-3-(O-carboxy-methyl)-oxime (T-3-CMO), 11 beta-hydroxytestosterone-11-carboxymethyl ether (T-11 beta-O-CME) and 19-hydroxytestosterone-19-carboxymethyl-ether (T-19-O-CME) were evaluated in enzyme immunoassays (EIAs) in combinations with penicillinase-labeled T-3-CMO, T-11 beta-O-CME, T-19-O-CME, and testosterone-17 beta-hemisuccinate (T-17 beta-HS) for their influence on the sensitivity and specificity of EIAs. Of the various combinations, anti-T-3-CMO antiserum along with T-11 beta-O-CME-penicillinase showed no cross-reaction with any of the closely related steroids, although the same antibody had 21.6% binding to 5 alpha-dihydrotestosterone (5 alpha-DHT) in radioimmunoassay. All the homologous combinations appeared to be less sensitive due to their low affinity for testosterone. It was also apparent that of all the heterologous systems tested, only two combinations, (a) anti-T-19-O-CME antiserum and T-3-CMO-penicillinase and (b) anti-T-3-CMO antiserum and T-11 beta-O-CME-penicillinase, were found to be more sensitive. The former was less specific; it showed 70% cross-reaction with 5 alpha-DHT. The ability of testosterone to displace the hapten-enzyme conjugate and the specificity of the assay appear to depend on the position of the enzyme label on the steroid molecule as well as on the availability of antigenic sites in particular combinations of antibody and hapten-enzyme conjugates.

Antibodies↗

Characterization and profiling of hepatic cytochromes P450 and phase II xenobiotic-metabolizing enzymes in beluga whales (Delphinapterus leucas) from the St. Lawrence River Estuary and the Canadian Arctic.

Cytochromes P450 (CYP, phase I) and conjugating (phase II) enzymes can be induced by and influence the toxicokinetics (metabolism) and toxicity of xenobiotic contaminants in exposed organisms. Beluga whale (Delphinapterus leucas) from the endangered St. Lawrence (SL) River Estuary population exhibit deleterious health effects and various severe pathologies that have been associated with contaminant exposure. In contrast, such effects (e.g. reproductive and immunological impairment) are generally less frequent in less exposed populations in the Canadian Arctic (CA). In the present study, opportunistic sampling resulted in the collection immediately after death of liver tissue from a single female neonate SL beluga (SL6) and male and female CA beluga (n=10) from the Arviat region of western Hudson Bay, in addition to sampling of stranded carcasses of male and female SL beluga (n=5) at least 12 h postmortem. We immunologically characterized cross-reactive proteins of hepatic microsomal CYP1A, CYP2B, CYP3A, CYP2E, epoxide hydrolase (EH) and uridine diphosphoglucuronosyl transferase (UDPGT) isozymes. Cross-reactive proteins were found in all SL and CA beluga using anti-rat CYP1A1, anti-rainbow trout CYP3A, anti-human CYP2E1, anti-rabbit EH and anti-human UDPGT1A1 polyclonal antibodies (Abs), whereas faintly cross-reactive CYP2B proteins were only found in SL6 and the CA samples using an anti-rabbit CYP2B1 Ab. In corresponding catalytic activity assessments, only SL6 and all CA beluga microsomal samples exhibited CYP1A-mediated 7-ethoxyresorufin O-deethylase (EROD) activity (51-260 pmol/mg/min), CYP3A-mediated activity (113-899 pmol/mg/min) based on the formation of 6beta-hydroxytestosterone using a testosterone hydroxylase assay, and UDPGT activity (830-4956 pmol/mg/min) based on 1-naphthylglucuronide formation. The marginal cross-reactivity with the anti-CYP2B1 Ab and lack of catalytically measurable hydroxytestosterone isomers associated with CYP2B-type activity in all the SL and CA animals is suggestive of low CYP2B-type enzyme expression in beluga. The absence of measurable total P450 enzyme levels and catalytic activities in samples from the stranded SL belugas suggested catalytically inactive enzymes as a consequence of tissue degradation related due to the time delay of sample collection after death. However, all SL and CA animals demonstrated similar, immunologically cross-reactive phase I and II hepatic enzyme profiles, which is suggestive of the importance of metabolism in the toxicokinetics and fate of xenobiotics in animals from both populations

Animals↗

Serum prolactin levels in castrated rams at various times of the year and during treatment with androgens or oestrogen.

Prolactin concentrations were measured in serum from wethers at various times of the year before and during treatment with testosterone proprionate, dihydrotestosterone propionate, 19-hydroxytestosterone dipropionate and oestradiol dipropionate. Levels of prolactin in serum were lower in untreated wethers during short (October) than during long (April-August) days. Seasonal differences persisted throughout the experiment but became less obvious during tretment with oestradiol dipropionate and 19-hydroxytestosterone dipropionate, both of which raised prolactin concentrations. Neither testosterone propionate nor dihydrotestosterone propionate altered the levels of prolactin.

Androgens↗

Theoretical kinetics of sequential metabolism in vitro. Study of the formation of 16 alpha-hydroxyandrostenedione from testosterone by purified rat P450 2C11.

P450 2C11 from rat liver is known to metabolize testosterone to 2 alpha-, 16 alpha-, and 6 beta-hydroxytestosterone, and to androstenedione and 16 alpha-hydroxyandrostenedione. Because Waxman (J. Biol. Chem. 259, 15481-15490) has reported that the enzyme converts androstenedione to 16 alpha-hydroxyandrostenedione, it seemed likely that the metabolite was formed from testosterone by way of androstenedione. Indeed, we have found that P450 2C11 does not convert 16 alpha-hydroxytestosterone to 16 alpha-hydroxyandrostenedione to any significant extent and, therefore, that the metabolite is formed from testosterone almost solely by way of androstenedione. To determine whether some of the 16 alpha-hydroxyandrostenedione might be formed directly from the androstenedione-enzyme complex, we developed an approach by which it is possible to calculate the amount of the androstenedione, released into the medium, relative to the amount of the androstenedione-enzyme complex that is converted directly to 16 alpha-hydroxyandrostenedione under initial conditions when the concentration of released androstenedione will be negligible. The approach uses two factors: factor A is the androstenedione/(androstenedione + 16 alpha-hydroxyandrostenedione) present at the end of the incubation, and factor B corrects for the amount of released androstenedione that recombines with the enzyme and is converted to 16 alpha-hydroxyandrostenedione. Although the values of both factors A and B will vary with the concentrations of testosterone and preformed androstenedione present in the incubation mixtures and with the duration of incubation, the value of A*B will be independent of these parameters.(ABSTRACT TRUNCATED AT 250 WORDS)

Androstenedione↗

Different testosterone metabolism by immortalized embryonic and postnatal hippocampal neurons from C57BL/6 mice: a crucial role for androstenedione.

Steroid hormones influence the development of undifferentiated brain during ontogenesis. In the present study we investigated the metabolic pathway of testosterone in immortalized embryonic and postnatal hippocampal neurons from C57BL/6 mice. Both cell lines are capable of metabolizing testosterone to 6alpha-hydroxytestosterone, 6beta-hydroxytestosterone and androstenedione. The formation was found to correlate with protein concentration and time of incubation. These linearities were significant for all metabolites except androstenedione that was the main metabolite in embryonic hippocampal neurons and nearly absent in postnatal neurons. Moreover, only embryonic cells react to testosterone with a decrease of beta-tubulin expression, that was a typical effect indicating induced neuronal maturation. Application of androstenedione caused the same decrease of beta-tubulin expression as testosterone did before. Our results of hippocampal testosterone metabolism in vitro confirm that not only estradiol and 5alpha-dihydrotestosterone could impact neural tissue but also androstenedione is a powerful metabolite involved in prenatal neuronal differentiation.

Androstenedione↗

Reversible and time-dependent inhibition of the hepatic cytochrome P450 steroidal hydroxylases by the proestrogenic pesticide methoxychlor in rat and human.

Methoxychlor, a currently used pesticide, is demethylated and hydroxylated by several hepatic microsomal cytochrome P450 enzymes. Also, methoxychlor undergoes metabolic activation, yielding a reactive intermediate (M*) that binds irreversibly and apparently covalently to microsomal proteins. The study investigated whether methoxychlor could inhibit or inactivate certain liver microsomal P450 enzymes. The regioselective and stereoselective hydroxylation of testosterone and the 2-hydroxylation of estradiol (E2) were utilized as markers of the P450 enzymes inhibited by methoxychlor. Both reversible and time-dependent inhibition were examined. Coincubation of methoxychlor and testosterone with liver microsomes from phenobarbital treated (PB-microsomes) male rats, yielded marked diminution of 2 alpha- and 16 alpha-testosterone hydroxylation, indicating strong inhibition of P4502C11 (P450h). Methoxychlor moderately inhibited 2 beta-, 7 alpha-, 15 alpha-, 15 beta-, and 16 beta-hydroxylation and androstenedione formation. There was only a weak inhibition of 6 beta-hydroxylation of testosterone. The methoxychlor-mediated inhibition of 6 beta-hydroxylation was competitive. By contrast, when methoxychlor was permitted to be metabolized by PB-microsomes or by liver microsomes from pregnenolone-16 alpha-carbonitrile treated rats (PCN-microsomes) prior to addition of testosterone, a pronounced time-dependent inhibition of 6 beta-hydroxylation was observed, suggesting that methoxychlor inactivates the P450 3A isozyme(s). The di-demethylated methoxychlor (bis-OH-M) and the tris-hydroxy (catechol) methoxychlor metabolite (tris-OH-M) inhibited 6 beta-hydroxylation in PB-microsomes competitively and noncompetitively, respectively; however, these methoxychlor metabolites did not exhibit a time-dependent inhibition. Methoxychlor inhibited competitively the formation of 7 alpha-hydroxytestosterone (7 alpha-OH-T) and 16 alpha-hydroxytestosterone (16 alpha-OH-T) but exhibited little or no time-dependent inhibition of generation of these metabolites, indicating that P450s 2A1, 2B1/B2, and 2C11 were inhibited but not inactivated. Methoxychlor inhibited in a time-dependent fashion the 2-hydroxylation of E2 in PB-microsomes. However, bis-OH-M exhibited solely reversible inhibition of the 2-hydroxylation, supporting our conclusion that the inactivation of P450s does not involve participation of the demethylated metabolites. Both competitive inhibition and time-dependent inactivation of human liver P450 3A (6 beta-hydroxylase) by methoxychlor, was observed. As with rat liver microsomes, the human 6 beta-hydroxylase was inhibited by bis-OH-M and tris-OH-M competitively and noncompetitively, respectively. Testosterone and estradiol strongly inhibited the irreversible binding of methoxychlor to microsomal proteins. This might explain the "clean" competitive inhibition by methoxychlor of the 6 beta-OH-T formation when the compounds were coincubated.(ABSTRACT TRUNCATED AT 400 WORDS)

Animals↗

The role of cytochrome 2B1 substrate recognition site residues 115, 294, 297, 298, and 362 in the oxidation of steroids and 7-alkoxycoumarins.

At least two substitutions were made at each of five amino acid residues in rat cytochrome P450 2B1 that align to residues of known importance in other P450s. The mutants were histidine tagged for purification from Escherichia coli, and the proteins were assessed for testosterone and 7-alkoxycoumarin oxidation. Alteration of each of the sites studied, Phe-115, Ser-294, Phe-297, Ala-298, and Leu-362, was found to affect overall enzyme activity or the metabolite profile. In particular, most of the mutants, excluding F297A, A298G, and L362F, exhibited significantly altered ratios of 16alpha-hydroxytestosterone:16beta-hydroxytestosterone, with the most dramatic alteration being displayed by A298V. Four 7-butoxycoumarin metabolites were produced by CYP2B1, of which two, 7-hydroxycoumarin and 7-(3-hydroxybutoxy)coumarin, were formed at nearly equal rates. Several mutants, F115A, F297A, F297I, and A298V, exhibited an increased predominance of one of the metabolites. The results from this study illustrate the conservation of functionally important residues across P450 subfamilies and families.

Amino Acid Substitution↗

Involvement of multiple biotransformation processes in the metabolic elimination of testosterone by juvenile and adult fathead minnows (Pimephales promelas).

Steroid hormone metabolic clearance pathways are susceptible to induction and suppression resulting from exposure to many xenobiotics. These biochemical effects have the potential to alter steroid hormone homeostasis and, ultimately, steroid hormone-dependent processes such as growth, development, and reproduction. In this study, the metabolic clearance of 17beta-hydroxy-4-androsten-3-one (testosterone) by adult male, adult female, and juvenile fathead minnows (Pimephales promelas) was evaluated. Individual elimination metabolites were identified and rates of metabolite elimination were quantified. Fathead minnows produced a variety of testosterone metabolites including oxido-reduced, hydroxylated, and conjugated derivatives. Metabolites identified by TLC/GC/MS included 4-androstene-3,17-dione (androstenedione), 17beta-hydroxy-5alpha-androstan-3-one (5alpha-dihydrotestosterone), 5alpha-androstane-3alpha,17beta-diol (3alpha-androstanediol), 5alpha-androstane-3beta,17beta-diol (3beta-androstanediol), 17beta-hydroxy-4-androstene-3,11-dione (11-ketotestosterone), 16beta-hydroxy-4-androsten-3-one (16beta-hydroxytestosterone), and 6beta-hydroxy-4-androsten-3-one (6beta-hydroxytestosterone). Testosterone and its metabolites were eliminated in both free and conjugated form. Adult male, adult female, and juvenile fathead minnows eliminated the same profile of testosterone metabolites. However, adult females eliminated androstanediols at a significantly greater rate than did males, and juvenile fish eliminated nearly all testosterone metabolites at greater weight-normalized rates than did adults. These results demonstrate that fathead minnows extensively metabolize testosterone leading to its elimination and provide the foundation upon which the effects of xenobiotics on testosterone metabolism can be assessed.

Aging↗

Bioreactor systems in drug metabolism: synthesis of cytochrome P450-generated metabolites.

In this communication, we report that suspension cultures of Sf21 insect cells, co-infected with baculovirus containing the cDNA for a single cytochrome P450 and NADPH-cytochrome P450 oxidoreductase, can be employed successfully as "bioreactors" for the synthesis of milligram quantities of cytochrome P450-generated metabolite(s). Three standard or probe substrates for the human P450s were chosen for the initial biosynthetic experiments: testosterone, diazepam, and diclofenac. Testosterone (100 microM, 2.88 mg/100 ml), added to a 100-ml CYP3A4 bioreactor, was converted to 6beta-hydroxytestosterone (2.3 mg) and 15beta-hydroxytestosterone (0.18 mg). Diazepam (100 microM, 2.9 mg/100 ml), added to a 100-ml CYP3A4 bioreactor, was converted to temazepam (1.1 mg), N-demethyldiazepam (0.35 mg), and oxazepam (0.15 mg). Diclofenac (100 microM, 3.18 mg/100 ml), added to a 100-ml CYP2C9 bioreactor, was converted to 4'-hydroxydiclofenac (2.6 mg). Since the goal for the development of the bioreactors was to provide a platform for both the production and subsequent purification of milligram quantities of P450-generated metabolite(s), a second 100-ml CYP2C9 bioreactor was used for the large-scale production and subsequent purification of 4'-hydroxydiclofenac. After 55 h of incubation, 7.95 mg of diclofenac was converted to 4.35 mg of 4'-hydroxydiclofenac, while 3.55 mg of unchanged diclofenac remained in the bioreactor. Using a simple preparative HPLC method, approximately 2.2 mg of 4'-hydroxydiclofenac and 1.9 mg of diclofenac were recovered from this experiment (28% yield). These results indicate clearly that suspension cultures of Sf21 insect cells coexpressing a cytochrome P450 and NADPH-cytochrome P450 oxidoreductase can be used effectively as bioreactors for the production and subsequent purification of milligram quantities of P450-derived metabolite(s).

Animals↗

Endosulfan elevates testosterone biotransformation and clearance in CD-1 mice.

Toxicant-mediated induction of hepatic biotransformation enzymes is a mechanism by which endogenous steroid hormone metabolism and elimination may be altered. Endosulfan, an organochlorine insecticide that has been demonstrated to induce hepatic P450 biotransformation enzymes, was examined for its ability to alter the rate of steroid hormone metabolism in CD-1 mice. Our objective was to evaluate whether endosulfan-induced changes in the rate of testosterone metabolism were reflected in the rate of testosterone clearance and if those alterations were sufficient to disrupt steroid hormone homeostasis within the animal. Major pathways for testosterone metabolism in the liver, including hydroxylation, conjugation to glucuronic acid or sulfate, and reduction/dehydrogenation, were examined for changes due to endosulfan exposure. In female mice, endosulfan treatment elicited a dose-dependent increase in the rate of total testosterone hydroxyl metabolite formation by selectively increasing the rate of production of 16 beta-, 6 alpha, and 16 alpha-hydroxytestosterone metabolites. The hydroxylation of testosterone in the 16 beta position was most sensitive to endosulfan with a 3.3-fold increase in the rate of production of this metabolite observed following exposure to 7.5 mg/kg/day for 7 days. The rate of testosterone dehydrogenation to androstenedione was increased by 7.5 mg/kg/day of endosulfan, but the rate of direct glucuronic acid or sulfate conjugation to testosterone was not affected by any of the dosages investigated. Endosulfan was generally more toxic to male mice and did not significantly alter the rate of total hydroxytestosterone metabolite formation or glucuronic acid or sulfate conjugation. The ability of endosulfan to enhance the elimination of testosterone was, therefore, investigated in female mice. Exposure of mice to 7.5 mg/kg/day of endosulfan resulted in an approximately 3.6-fold increase in the rate of urinary elimination of [14C]androgen, but had no significant effect on the fecal elimination of [14C]androgen. The increase in androgen clearance was associated only with a small, nonsignificant decrease in serum testosterone levels. Results indicate that increases in testosterone biotransformation from endosulfan exposure can result in increases in the elimination of the steroid. However, homeostatic processes apparently compensate for the effect and minimize any consequences on serum hormone levels.

Animals↗

DNA binding, adduct characterisation and metabolic activation of aflatoxin B1 catalysed by isolated rat liver parenchymal, Kupffer and endothelial cells.

In vitro studies with rat liver parenchymal, Kupffer and endothelial cells isolated from male Sprague-Dawley rats were undertaken to investigate cell-specific bioactivation of aflatoxin B1, DNA binding and adduct formation. In the mutagenicity studies, using homogenates of all three separated liver cell populations (co-incubated with NADP+ and glucose-6-phosphate as cofactors for the cytochrome P-450 monooxygenase system) parenchymal, Kupffer and endothelial cells were able to activate aflatoxin B1 to a metabolite mutagenic to Salmonella typhimurium TA 98. In the case of nonparenchymal cells (i.e. Kupffer and endothelial cells) 10-fold higher concentrations of aflatoxin B1 had to be used to obtain a similar number of revertants to that observed with parenchymal cells. Induction studies with Aroclor 1254 led to a striking decrease in the activation of aflatoxin B1 in parenchymal cells, whereas nonparenchymal cells had a slightly enhanced metabolic activation capacity for aflatoxin B1. Metabolism studies with microsomes from induced and noninduced cells using testosterone as substrate revealed comparable results: after induction with Aroclor 1254, parenchymal cells showed a 60% decrease in the formation rate of 2 alpha-hydroxytestosterone, whereas the formation rate of this metabolite remained unchanged in nonparenchymal cells; 2 alpha-hydroxytestosterone is specifically formed by cytochrome P-450 IIC11, which also catalyses the activation of aflatoxin B1 to its epoxide. When freshly isolated, intact cells were incubated with tritiated aflatoxin B1, a dose-dependent aflatoxin B1 binding to DNA in parenchymal and nonparenchymal cells was observed. HPLC analysis of DNA acid hydrolysates of all three cell types showed the major adduct to be 8,9-dihydro-8-(N7-guanyl)-9-hydroxy-aflatoxin B1.

Aflatoxin B1↗

Isozyme specificity of testosterone 7 alpha-hydroxylation in rat hepatic microsomes: is cytochrome P-450a the sole catalyst?

In the present study we show that monospecific antibody against cytochrome P-450a completely inhibits testosterone 7 alpha-hydroxylation in hepatic microsomes of untreated male or female rats or rats of either sex treated with dexamethasone. These data are in contrast with those of K. Nagata et al. (1987, J. Biol. Chem. 262, 2787-2793) who recently reported that an antibody prepared against cytochrome P-450a completely inhibited testosterone 7 alpha-hydroxylase activity in microsomes from untreated or 3-methylcholanthrene-treated rats but only inhibited 50% of the activity in microsomes from dexamethasone-treated rats. They proposed that dexamethasone treatment of rats induced another testosterone 7 alpha-hydroxylase in rat liver. The discrepancy in the two sets of data was due, at least in part, to the use of a chromatography system by Nagata et al. that is incapable of resolving a number of testosterone metabolites. Dexamethasone treatment of rats leads to a marked increase in the production of several testosterone metabolites, including 15 beta-hydroxytestosterone which is cochromatographic with 7 alpha-hydroxytestosterone in their chromatography system. Our results indicate that cytochrome P-450a accounts for all of the testosterone 7 alpha-hydroxylase activity in microsomes from dexamethasone-treated rats, and that testosterone 7 alpha-hydroxylation continues to be a useful marker for monitoring cytochrome P-450a in rat hepatic microsomes.

Animals↗

Influence of estradiol and testosterone on cytochrome P-450 and monooxygenase activity in immature brook trout, Salvelinus fontinalis.

Levels of hepatic microsomal cytochrome P-450 were depressed by administration of estradiol-17 beta and were elevated by administration of testosterone in both male and female juvenile brook trout (Salvelinus fontinalis). Treatment-associated changes in the levels of other microsomal electron transfer components in liver did not reflect the changes in cytochrome P-450 content and were also distinct from the changes in these components in kidney. Electrophoretic analysis of hepatic microsomes revealed that estradiol treatment reduced the amounts of several proteins including some heme-staining protein at 56,000 daltons, possibly containing cytochrome P-450. Hepatic microsomal benzo[a]pyrene hydroxylase and the response to 7,8-benzoflavone in vitro were affected little by steroid treatment, and ethoxyresorufin O-deethylase activity could not be detected in any of the samples. Hepatic microsomes metabolized testosterone to a suite of products including 6 beta-hydroxytestosterone (the major metabolite) and 16 beta-hydroxytestosterone, plus as many as eleven unknown metabolites. Estradiol-17 beta treatment depressed the rates of testosterone metabolism and particularly the rates of 6 beta-hydroxylase activity but did not affect 16 beta-hydroxylase activity. Both activities were largely unaffected by testosterone. The results are consistent with the idea that both androgens and estrogens regulate the levels of hepatic cytochrome P-450 in brook trout and that the effect, at least of estradiol-17 beta, involves regulation of forms that function in specific hydroxylation of testosterone. The significance of these effects and whether factors additional to steroids are involved in this regulation of hepatic cytochromes P-450 in fish remain to be established.

Animals↗