Adaptive responses of rat liver to the gestagen and anti-androgen cyproterone acetate and other inducers. III. Cytological changes

Treatment of rats with cyproterone acetate (CPA) induces liver growth. Intact hepatocytes and cell nuclei were isolated from enlarged livers and their volumes or diameters were determined by electronic and microscopic methods. No changes in mean hepatocyte volume or ploidy were observed. However, there was a marked fall in the frequency of binuclear hepatocytes (from 43% to 7%) and a concomitant increase of nuclear ploidy. This effect probably resulted from CPA-induced replication of binuclear hepatocytes. The total number of hepatocytes replicating in response to CPA was estimated on the basis of these data and was found to be up to 75% of all parenchymal cells. Similar cytological changes were observed in the liver after treatment with pregnenolone-16 alpha-carbonitrile (PCN) and, to a lesser extent, with alpha-hexachlorocyclohexane (alpha-HCH). In contrast, physiological liver growth in adolescent rats was characterized by only small changes in binuclearity and nuclear ploidy, and by increases of cellular ploidy. Thus, ploidy analyses may be a useful tool to characterize the type of growth stimulation. Following discontinuation of treatment the cytological changes induced by CPA or alpha-HCH were not reversible in a matter of 3 weeks.     

Unusual patterns of benzo[a]pyrene metabolites and DNA-benzo[a]pyrene adducts produced by human placental microsomes in vitro

Human placental microsomes were incubated with [³H]benzo[a]pyrene (BP) and Salmon sperm DNA and the resulting metabolite-nucleoside complexes resolved by Sephadex LH-20 chromatography. The metabolite pattern was analyzed by high-pressure liquid chromatography (HPLC). The incubates were also co-chromatographed with extracts obtained from incubates with rat liver microsomes and [¹⁴C]BP. Phenols, quinones and 7,8-dihydrodiol were detected in the placental incubates. Both 9,10- and 4,5-dihydrodiols were very low as compared with control rat liver samples. Placental microsomes catalyzed the binding of BP metabolites to DNA in vitro, giving rise to two main complexes which co-chromatographed with rat liver-produced peaks attributable to 7,8-diol-9,10-epoxide and 7,8-oxide and/or quinones when metabolized further. The nucleoside metabolite peaks attributable to 4,5-oxide and 9-phenol-4,5-oxide were lacking when compared with the binding pattern catalyzed by rat liver. Both the total binding and specific metabolite-nucleoside adducts in the placenta correlated with fluorometrically measured aryl hydrocarbon hydroxylase (AHH) activity and with the amount of dihydrodiol formed. The results demonstrate that both the metabolite pattern and the nucleoside-metabolite complexes formed by the placental microsomes in vitro differed greatly from those produced by rat liver microsomes. These studies also suggest that it is not possible to predict specific patterns of DNA binding from AHH measurements or even from BP metabolite patterns, especially when comparing different tissues and species.     

Morphine metabolism revisited: I. Metabolic activation of morphine to a reactive species in rats

Treatment of fasted rats with relatively high doses of morphine rapidly results in depletion of hepatic glutathione (GSH) content and marked elevation of serum transaminase activity. Such morphine-induced response has been generally attributed to central nervous system mediated effects of the drug. We now report that this response might be due to a direct effect of the drug in the liver. That is, its metabolic activation to reactive electrophilic metabolite(s), by the hepatic cytochrome P-450-dependent mixed function oxidase system. Structure-activity relationships of morphine and its congeners indicate that the (-)-3-hydroxy-N- methylmorphinan moiety is linked with the potential of these opioids to deplete hepatic GSH and to raise serum transaminases in rats.     

The influence of five monooxygenase inducers on liver cytosol estradiol receptor levels in the ovariectomized adult rat

The intraperitoneal injection of the well known monooxygenase inducers (phenobarbital, β-naphtoflavone, pregnenolone-16α-carbonitrile, benzo(a)-pyrene, methylcholanthrene) elicits a net decrease in the specific binding of estradiol to its cytosol receptor in female rat livers. Amongst the five chemicals tested, only phenobarbital did not exhibit such a phenomenon, but caused a slight increase. This observation was neither due to a competitive inhibition by these compounds, nor to an enhanced metabolism of [³H]-estradiol. Moreover, when this effect was produced by polycyclic hydrocarbons, it was inversely correlated to the activity of aryl hydrocarbon hydroxylase, induced by these same chemicals.     

Polyhalogenated biphenyls and phenobarbital: evaluation as inducers of drug metabolizing enzymes in the sheepshead, Archosargus probatocephalus

Several doses of Aroclor 1254 (polychlorinated biphenyl (PCB) mixture), Firemaster FF1 (polybrominated biphenyl (PBB) mixture), 2,2',4,4',5,5'-hexabromobiphenyl (HBB), 3,3',4,4',5,5'-hexachlorobiphenyl (HCB) and phenobarbital (PB) were administered to the marine fish sheepshead (Archosargus probatocephalus). The PCB and PBB mixtures caused induction of hepatic microsomal benzo[a]pyrene hydroxylase (AHH), 7-ethoxycoumarin O-deethylase (7-EC) and 7-ethoxyresorufin O-deethylase (ERF) activities, but not benzphetamine N-demethylase (BND), epoxide hydrolase (EH) or glutathione S-transferase (GSH-T) activities. This induction pattern is typical of that caused by polycyclic aromatic hydrocarbons (PAH) in fish and mammals or by tetrachlorodibenzo-p-dioxin (TCDD) in mammals. The extent of induction of AHH-activity and cytochrome P-450 content was higher when experiments were carried out in summer (water temperature 25 +/- 4 degrees C) than in winter (water temperature 11 +/- 3 degrees C). Firemaster FF1 (15 mg/kg) induced fish for at least 56 days in both summer and winter at which time the liver concentrations of PBB were in the ppm range. PCB concentrations in the ppm range have been found in fish from polluted lakes and seas, thus we may expect that environmental exposure to PCB is sufficient to induce hepatic mixed function oxidase (MFO) activities. The PCB isomer 3,3'4,4'5,5'-HCB, which induces the same spectrum of hepatic drug-metabolizing activities as TCDD and PAH in rats, had a broadly similar effect in the sheepshead. Another purified isomer, 2,2',4,4',5,5'-HBB, which induces the same enzymes as PB in rats, had no effect on drug-metabolizing activities in sheepshead. PB was also without effect on sheepshead hepatic drug-metabolizing enzymes, although a typical narcotic effect was produced in PB-treated sheepshead. Our studies provide further evidence that drug-metabolizing activities in fish liver are readily induced by chemicals like TCDD or PAH, but we fail to demonstrate induction after treatment of sheepshead with inducers of the PB type.     

Interrelationships in mice of antipyrine half-life, hepatic monooxygenase activities and liver S9-mediated mutagenicity of aflatoxin B1, benzo[alpha]pyrene 7,8-dihydrodiol, 2-acetylaminofluorene and N-nitrosomorpholine

To evaluate the predictive value of serum antipyrine half-life AP(T1/2) as an index of hepatic carcinogen metabolism, groups of C57BL/6 and DBA/2 mice were treated with various inducers and inhibitors of cytochrome P-450-dependent monooxygenases (pregnenolone-16 alpha-carbonitrile (PCN), phenobarbital (PB), 5,6-benzoflavone (5,6-BF), 3-methylcholanthrene (MC), disulfiram (DIS), 7,8-BF). Groups of mice were also given ethanol (3% in drinking water) for 12 days. Within each group, mean serum AP-(T1/2) was compared with (i) the in vitro activity of hepatic microsomal benzo[alpha]pyrene (BP) 3-hydroxylase, 2-acetylaminofluorene (AAF)-N-hydroxylase and aldrin monooxygenase, and (ii) the liver S9-mediated mutagenicity of aflatoxin B1 (AFB), trans-7,8-dihydro-7,8-dihydroxybenzo[alpha]pyrene (BP 7,8-diol), 2-acetylaminofluorene and N-nitrosomorpholine (NMOR) in Salmonella typhimurium strains. Serum AP(T1/2) was only correlated negatively with the activity of BP 3-hydroxylase (P less than 0.001) and aldrin monooxygenase (P less than 0.001). No statistically significant correlation was found between serum AP(T1/2) and liver S9-mediated mutagenicity for any of the four carcinogens. On the basis of these results, we conclude that serum AP(T1/2) may not be a reliable index of the capacity of liver to convert carcinogens into reactive intermediates.