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The induction of cytochrome P-450 and monooxygenase activities in the chick embryo by 2-acetylaminofluorene.

Administration of 2-acetylaminofluorene to chick embryos increases the cytochrome P-450 level 3.4 fold but causes no increase in total epoxide hydrase activity or other microsomal electron transport enzymes. The induction response shows some similarity to that elicited by phenabarbitone both in terms of the monooxygenase activities induced and their inhibition characteristics. Induction of a specific cytochrome P-450 subform by this agent may increase its detoxification and in part account for the resistance of avian species to its hepatocarcinogenic effect.

2-Acetylaminofluorene↗

Induction of rat hepatic cytochromes P-450 by environmental nitropolycyclic aromatic hydrocarbons.

Nitrated polycyclic aromatic hydrocarbons (PAHs) are environmental contaminants that result from various incomplete combustion processes. We have examined the activity of hepatic microsomal enzymes in rats pretreated with a series of environmentally occurring nitrated PAHs including: 1- and 4-nitropyrene, 1,3-, 1,6- and 1,8-dinitropyrene, 6-nitrochrysene, 7-nitrobenz[a]anthracene, 3-nitrofluoranthene, and 1-, 3-, and 6-nitrobenzo[a]pyrene. None of the compounds increased the cytochrome P-450 content more than 2-fold. 1,8-Dinitropyrene, 6-nitrochrysene, and 1- and 3-nitrobenzo[a]pyrene significantly increased arylhydrocarbon hydroxylase activity 2- to 8-fold higher than solvent-treated controls. The induction of 7-ethoxycoumarin O-deethylase activity paralleled that found with arylhydrocarbon hydroxylase. The maximum induction of aminopyrine N-demethylase was only 1.5-fold, and none of the nitrated PAHs caused significant increases in epoxide hydrase or NADPH-cytochrome c reductase. 1-Nitropyrene reductase activity was induced by each of the compounds with the exception of 6-nitrobenzo[a]pyrene. The greatest increase was caused by 1-nitrobenzo[a]pyrene followed by 1,3-dinitropyrene, 3-nitrobenzo[a]pyrene and 6-nitrochrysene. These data suggest that nitrated PAHs may potentiate the effects of subsequent exposures to various chemical carcinogens.

7-Alkoxycoumarin O-Dealkylase↗

Induction of sister chromatid exchanges by styrene and its presumed metabolite styrene oxide in the presence of rat liver homogenate.

Styrene and its metabolite styrene oxide were tested for their ability to induce sister chromatid exchanges (SCE) in CHO cells. Styrene oxide appeared to be a potent inducer of SCE. Styrene itself did not increase the number of SCE per metaphase, even in the presence of a metabolic activation system. The metabolic activation system decreased the SCE induction caused by styrene oxide. Induction of SCE by styrene in the presence of metabolic activation occurred when cyclohexene oxide was used as an inhibitor of the enzyme epoxide hydrase.

Animals↗

Evidence for the involvement of a diol-epoxide in the binding of 7,12-dimethylbenz(a)anthracene to DNA in cells in culture.

1,1,1-Trichloropropene 2,3-oxide (TCPO), a known inhibitor of the enzyme epoxide hydrase, inhibits binding of the carcinogen, 7,12-dimethylbenz(a)anthracene (DMBA), to the DNA of secondary mouse embryo cell cultures under conditions which do not appreciably decrease the overall metabolism of this carcinogen. This suggests that the formation of a transdihydrodiol is a necessary step in the metabolic pathway leading to DNA binding and that binding probably occurs through the generation of a reactive diol-epoxide. In concert with this, the major DMBA-DNA product isolated by chromatography on Sephadex LH-20 eluted with a methanol-water gradient is resolved into two separate components in a methanol-sodium borate solution gradient suggesting that, as is known for benzo(a)pyrene, two stereoisomeric diol-epoxides are involved in the binding of DMBA to DNA.

9,10-Dimethyl-1,2-benzanthracene↗

Activation of [14C] chlorobiphenyls to protein-binding metabolites by rat liver microsomes.

The irreversible binding of [14C] 2,2'-di- and [14C] 2,4,5,2',4',5'-hexachlorobiphenyl ([14C] DCB and [14C] HCB) to protein was studied in the presence of rat liver microsomes and a NADPH-generating system. Protein-bound radioactivity was found with [14C] DCB but not with [14C] HCB. The binding of 14C-metabolites was increased by pretreatment of the rats with phenobarbital or polychlorinated biphenyls. Protein binding was linear for 80 min. In contrast, monohydroxy-metabolites of DCB were formed and degraded within 40 min. Inhibition of secondary oxidation of DCB by scavenging superoxide anions or by glucuronidation of the monophenols markedly decreased the protein binding. Addition of trichloropropene oxide or styrene oxide, both inhibitors of epoxide hydrase, did not significantly stimulate the binding. The results suggest that the majority of reactive metabolites of DCB arise from secondary metabolism, i.e., the subsequent oxidation of the phenolic metabolites. Arene oxides, the primary products, appear to play a minor role in the protein binding of DCB.

Albumins↗

Epoxide metabolizing enzyme activities in rat testes: postnatal development and relative activity in interstitial and spermatogenic cell compartments.

Microsomal epoxide hydrase (EH) and 176 000 g supernatant fraction glutathione-S-transferase (GSH-S-T) activities were determined with styrene oxide as substrate in rat testes during postnatal development. The development of these enzymes was also followed in liver for comparison. Testes of 6-day-old rats had high GSH-S-T activities (66 nmol/min/mg protein), which were about 50% of the adult levels. Transferase activity then developed slowly and reached a maximum by 165 days of age. Specific testicular GSH-S-T activities of 6-day-old rats were 3--4 times those of hepatic GSH-S-T activities in the same animals. In contrast, EH activities of both liver and testes were very low in prepubertal rats, but they increased dramatically at the onset of puberty and reached maximum activities by 45 days of age. Microsomal and microsomal supernatant fractions prepared from adult rat spermatogenic cells had about twice the EH and GSH-S-T specific activities (with styrene oxide or benzo[a]pyrene 4,5-oxide as substrates) of similar fractions prepared from interstitial cells. On the other hand, benzo[a]pyrene hydroxylase (AHH) activity and cytochrome P-450 content were at least 2-fold greater in microsomes from interstitial cells than in those from spermatogenic cells.

Aging↗

Fate of juvenile hormone in mammalian cell culture.

The metabolism of juvenile hormone (JH) I has been examined in fetal mouse liver cells maintained in culture. Diffusion of the hormone into the cells appears to be passive. The hormone is metabolized essentially to organic-soluble metabolites (diol ester, diol acid and acid) by the action of epoxide hydrase and carboxylesterases. Conjugative reactions play a minor role, less than 3% of the hormone being excreted as conjugates (glucuronides, sulfates and mercapturic acid). About 0.8% of the cellular radioactivity is bound to macromolecules, mainly those of nuclear and mitochondrial origin. Metyrapone and SKF 525-A inhibit covalent binding of the hormone to cytoplasmic macromolecules, which suggests participation of the cytochrome P-450 system in covalent binding of the hormone.

Animals↗

Absolute stereochemistry of the trans-dihydrodiols formed from benzo[a]anthracene by liver microsomes.

Through application of the exciton chirality method, absolute stereochemistry has been assigned to the (+)-and (-)-enantiomers of four of the five metabolically possible trans-dihydrodiols of the polycyclic hydrocarbon benzo[a]anthracene (BA). The (+)- and (-)-enantiomers of each of these dihydrodiols can be separated as their diastereomeric bis-esters with (-)-alpha-methoxy-alpha-trifluoromethylphenylacetic acid by high pressure liquid chromatography (HPLC). BA 3,4-, 5,6-, 8,9- and 10,11-dihydrodiol are formed in 38%, 36%, 78% and 66% enantiometric purity, respectively, by liver microsomes from phenobarbital-treated rats, whereas the liver microsomes from 3-methylcholanthrene(MC)-treated rats form BA 5,6-, 8,9- and 10,11-dihydrodiols with higher optical purity (62%, 96% and 96%, respectively). BA 3,4-dihydrodiol is formed from (+/-)-BA 3,4-oxide by microsomal epoxide hydrase in very high enantiometric purity (78%). The major enantiomer of the BA dihydrodiols formed by liver enzymes has R,R absolute stereochemistry in each case. In parallel with previous studies on the metabolism of benzo[a]pyrene, the more tumorigenic (-)-enantiomer is the predominant isomer of BA 3,4-dihydrodiol formed by liver microsomes from BA.

Animals↗

Nuclear metabolism. I. Determination of styrene monooxygenase activity in rat liver nuclei.

Styrene monooxygenase activity was measured in intact nuclear preparations from rat liver by means of a gas chromatographic method. Styrene epoxide formation is NADPH-dependent although it is enhanced when NADH is added with NADPH. This activity is inhibited by microsomal monooxygenase inhibitors SKF 525A and metyrapone and by microsomal epoxide hydrase inhibitors 1,2-epoxy-3,3,3-trichloropropene oxide and cyclohexene oxide. The percentage of inhibition is quantitatively different for the four compounds. Known inducers of liver microsomal monooxygenase show different patterns of induction on nuclear preparations. Phenobarbital induces nuclear monooxygenase activity more than the respective microsomal activity, whereas the contrary holds true for beta-naphthoflavone.

Animals↗

Identification of an arene oxide metabolite of 2,2',5-5'-tetrachlorobiphenyl by gas chromatography-mass spectroscopy.

Tritiated 2,2'5,5'-tetrachlorobiphenyl (3H-TCB) was incubated with phenobarbital(PB)-induced rat liver microsomes in the presence of an epoxide hydrase inhibitor and brominated analog (BrAO) of the expected metabolic intermediate, 2,2',5,5'-tetrachlorobiphenyl-3,4-oxide (TCBAO). A putative arene oxide intermediate (3H-AO), which was radiolabeled, was separated from 3H-TCB and BrAO by column chromatography, high pressure liquid chromatography (HPLC) and thin-layer chromatography (TLC), and was analyzed for TCBAO by methods that were independent of radiometric techniques. The retention times (Rt's) of TCBAO and 3H-AO on two gas chromatography (GC) columns were the same, both before and after acid catalyzed rearrangement. 3H-AO was further characterized by rearrangement to a mixture of 3- and 4-hydroxy-TCB that was identified by gas chromatography-mass spectroscopy (GC-MS). The rate of TCB metabolism and the production of 3H-AO by liver microsomes from a PB-induced, adult male rhesus monkey was less than that observed with rat microsomes. The 3H-AO from the monkey was also characterized as TCBAO by rearrangement to the characteristic TCB phenols that were analyzed by GC-MS using selective ion monitoring. This study is the first in which an arene oxide of a polychlorinated biphenyl (PCB) was actually isolated as a mammalian metabolite and subjected to direct chemical analysis.

Animals↗

Effect of particulates on metabolism and mutagenicity of benzo[a]pyrene.

Mechanisms of co-carcinogenicity of particulates, such as iron oxide and asbestos, and benzo[a]pyrene (B[a]P) are not completely understood. Particulates dramatically alter rates of uptake of B[a]P into membranes, a factor which could account for co-carcinogenicity. However, B[a]P must be activated to reactive forms to be carcinogenic and mutagenic so alterations in metabolism of B[a]P by particulates also could result in co-carcinogenesis. To elucidate mechanisms of particulate-B[a]P co-carcinogenesis, we have correlated rates of uptake of B[a]P into microsomes with metabolism of B[a]P and with mutagenicity of B[a]P in the Ames test. In general, aryl hydrocarbon hydroxylase (AHH) activity paralleled rates of uptake of B[a]P, though some inhibition of AHH activity by particulates which was not attributable to availability of B[a]P was evident. This inhibition was studied further by assaying separately mixed function oxidase and epoxide hydrase activities in the presence of particulates. Both chrysotile and iron oxide inhibited O-deethylation of 7-ethoxyresorufin and hydration of B[a]P-4,5-oxide. To determine effects of this inhibition on activation of B[a]P to reactive forms, we studied profiles of metabolites of B[a]P and mutagenicity of B[a]P. The only alteration in profiles of B[a]P metabolites produced by particulates was that due to effects on rates of uptake. Similarly, mutagenicity of B[a]P was positively correlated with rates of uptake into microsomes. We conclude that the predominant effects of chrysotile and iron oxide are in altering rates of uptake of particle-adsorbed B[a]P. Changes in uptake rates then result in alterations of B[a]P metabolism and mutagenicity.

Adsorption↗

Effect of tauroursodeoxycholic and ursodeoxycholic acid on ethanol-induced cell injuries in the human Hep G2 cell line.

BACKGROUND & AIMS: Taurodeoxycholic acid (TUDCA) and ursodeoxycholic acid (UDCA) exert a protective effect in chronic cholestasis. This study reports the effect of TUDCA and UDCA on an in vitro model for ethanol-induced liver damage. METHODS: Hep G2 cells were incubated for 24 hours with 80 mmol/L ethanol in the presence or absence of 50 mumol/L TUDCA or UDCA. Cells were also pretreated with 80 mmol/L EtOH and then exposed to 50 mumol/L bile acids. Cytotoxicity was assessed by the metabolism of formazan (3-(4,5-dimethyl-thiazol-2-yl)-2, 5-diphenyl tetrazolium bromide and sodium 3,3'-(phenylamino) carbonyl-3,4-tetrazolium-bis (4-methoxy-6-nitro) benzene sulfonic acid hydrase and by the release into the culture medium of different enzymes (aspartate aminotransferase, glutamate dehydrogenase, gamma-glutamyl transferase, and lactate dehydrogenase). RESULTS: The incubation of Hep G2 with EtOH significantly (P < 0.001) increased cytotoxicity. Both TUDCA or UDCA reduced cytoxicity to a similar extent (P < 0.001). Cells pretreated with EtOH and then added with TUDCA or UDCA responded differently because TUDCA was significantly more effective (P < 0.05) than an equimolar dose of UDCA in reversing the damage. Electron microscopic examination revealed that TUDCA and UDCA were both able to prevent mitochondrial damage and to reduce steatosis induced by EtOH. CONCLUSIONS: Low doses of TUDCA and UDCA protect Hep G2 cells from EtOH-induced cytotoxicity. However, TUDCA seems to be more effective than UDCA in reversing the damage.

Cell Survival↗

Activation of polycyclic hydrocarbons in Reuber H4-II-E hepatoma cells. An in vitro system for the induction of SCEs.

Activation of polycyclic aromatic hydrocarbons (PAHs) was examined in the Reuber H4-II-E established cell line without the use of exogenous enzyme preparations. Metabolism of PAHs to genotoxic products was determined by the induction of sister-chromatid exchanges (SCEs). The induction of SCEs followed a dose-response pattern with plateaus at high doses of PAH. The effects of metabolic enzyme inducers (3-methylcholanthrene, phenobarbital, Aroclor 1254) and the epoxide hydrase inhibitor 1,1,1-trichloropropylene oxide were assessed as changes in SCE induction and enhanced production of water-soluble metabolites. Results indicate that Reuber H4-II-E cells can be employed in the testing of carcinogens activated by the P1-450 monooxygenase system and would be a useful in vitro system for the study of mechanisms of metabolic induction and their effect on genetic toxicity.

9,10-Dimethyl-1,2-benzanthracene↗

Covalent binding of [14C]methoxychlor metabolite(s) to rat liver microsomal components.

[14C]Methoxychlor was incubated with NADPH-fortified liver microsomes from male rats, and covalent binding to microsomal components was determined. The binding process was markedly enhanced when microsomes from phenobarbital-treated rats were employed. However, when microsomes from methylcholanthrene-treated rats were used the level of binding was not significantly affected. Incubation in the presence of glutathione, cysteine, or ascorbate markedly diminished binding. Metyrapone and SKF 525-A, inhibitors of hepatic cytochrome P-450-linked monooxygenase activity, inhibited the binding. Also, ethylmorphine and hexobarbital, alternate substrates of the monooxygenase system, inhibited binding. There was no binding to microsomal components in the absence of NADPH or oxygen. TCPO (1,1,1-trichloropropane-2,3-oxide), an inhibitor of epoxide hydrase activity, failed to enhance the binding process. However, N,N'-diphenyl-p-phenylenediamine (NDP) and n-propyl gallate (PG), both free radical scavengers, decreased binding at micromolar concentrations without altering the extent of formation of polar [14C]methoxychlor metabolites. It was concluded that methoxychlor undergoes a hepatic microsomal monooxygenase(s)-mediated activation and that the resultant reactive metabolites (possibly free radicals) bind covalently to microsomal components. By contrast, the binding resulting from the incubation of an impure mixture of polar [14C]methoxychlor metabolites with liver microsomes did not require NADPH and O2 and was not affected by NDP, Pg, ascorbate, or heat-treatment of microsomes. This finding suggested that the binding subsequent to the initial metabolic activation of methoxychlor does not require further enzymatic transformation. However, whether the binding with metabolites represents the same chemical species as the binding with [14C]methoxychlor remains to be established.

Animals↗

Resolution by DEAE-cellulose chromatography of the enzymatic steps in the transformation of arachidonic acid into 8, 11, 12- and 10, 11, 12-trihydroxy-eicosatrienoic acid by the rat lung.

The 30-50% ammonium sulfate fraction of the high speed supernatant (100,000 xg) of a rat lung homogenate is capable of catalysing the conversion of arachidonic acid into 8,11,12- and 10,11, 12-trihydroxyeicosatrienoic acids. This enzyme preparation was resolved through DEAE cellulose chromatography into three stages which were assayed with precursors specific for each stage. Thus in the first stage arachidonic acid is converted by 12-lipoxygenase into 12-hydroperoxy-5,8,10,14-eicosatetraenoic acid (12-HPETE) detected as the corresponding 12-hydroxy product (12-HETE). 12-HPETE in turn is converted into 8-hydroxy-11,12-epoxy-5,9,14-eicosatrienoic acid and 10-hydroxy-11,12-epoxy-5,8,14-eicosatrienoic acid. These epoxides are in turn selectively converted through an epoxide hydrase into the respective triols. While the first and third stages were carried out by distinct fractions from the DEAE columns, the second i.e. conversion of 12-HPETE into epoxides, was detected in all fractions as was the reduction of 12-HPETE into 12-HETE.

12-Hydroxy-5,8,10,14-eicosatetraenoic Acid↗

The aza-arenes as mutagens for Salmonella typhimurium.

Several unsubstituted aza-arenes have been found to be more mutagenic to Salmonella typhimurium than their corresponding parent hydrocarbons. In most cases, the activity of these compounds depended on the presence of a post-mitochondrial supernatant for metabolic activation, although acridine was mutagenic only in the absence of such an activating system. An examination of the effect of the metabolizing system's concentration on mutagenicity showed that quinoline, benzo[f]quinoline, and phenanthridine have different optima. In an attempt to uncover active intermediates in aza-arene metabolism, N-oxides of quinoline and phenanthridine were synthesized and found to be non-mutagenic, and coincubation with the epoxide hydrase inhibitor trichloropropylene oxide did not affect the mutagenic activity of quinoline or phenanthridine.

Animals↗

Effect of induction by DDT on metabolism and mutagenicity of benzo[a]pyrene.

Liver microsomal enzymes are essential for the detection of benzo[a]pyrene (B[a]P)-mediated mutagenesis in the Salmonella/mammalian microsome mutagenicity test and, furthermore, this mutagenicity is considerably enhanced by induction of hepatic enzymes involved with drug metabolism. Although Aroclor 1254 is most commonly used for induction of S9 enzymes, DDT is also capable of this induction. This paper reports a comparison of liver S9 fraction induced by the two agents: there is a marked difference in their concentration optima for metabolism of B[a]P; greater numbers of revertant colonies are seen with Aroclor-induced S9, which is optimal at a concentration of 10% (v/v), whereas DDT-induced S9 is optimal at 2.5% (v/v); Aroclor induces aryl hydrocarbon hydroxylase (AHH), cytochrome P-450 and epoxide hydrase while DDT induces only AHH, to about half the level detected in the Aroclor-induced S9 fraction. A comparison of metabolite distribution for Aroclor- and DDT-induced hepatic microsomes reveals quantitative differences only. DDT-induced microsomes yield a greater proportion of B[a]P-4,5-oxide and its metabolic product B[a]P-4,5-dihydrodiol than do Aroclor-induced microsomes. Time course studies on the mutagen half-life measured on the agar plate provides good evidence that metabolites responsible for mutagenicity were different for each inducer.

Animals↗

Acute cytogenetic effect of benzene on rat bone marrow cells in vivo and the effect of inducers or inhibitors of drug-metabolizing enzymes.

Acute cytogenetic effects of benzene in LE rat bone marrow cells in vivo were studied. Chromosome aberrations (CA) induced by benzene consisted mainly of gaps and breaks. Cells with exchanges were rarely observed. The incidence of benzene-induced CA was at its maximum level 12 h after the p.o. or i.p. administration of benzene, dependent on the dose of benzene administered, and higher in male rats than in female rats. However, the sex difference was not observed in the repeated inhalation experiment. Chromosome damage was higher with the p.o. than the i.p. administration. LE rats were more sensitive than Wistar and SD rats to the clastogenic action of benzene. Phenobarbital and Sudan III are well known as inducers of drug-metabolizing enzymes. The peak percentage of benzene-induced CA in the rats pretreated with phenobarbital was observed 6 h after the benzene injection, and it occurred at a higher level than in the rats given only benzene. On the other hand, Sudan III pretreatment suppressed benzene-induced CA at all periods after the benzene injection. SKF-525A (a cytochrome P-450 inhibitor) and cyclohexene oxide (an epoxide hydrase inhibitor) pretreatment also suppressed benzene-induced CA.

Animals↗