Differential effect of several inducers on hepatic and mammary benzo(A)pyrene metabolism in rat and hamster

Possible Application of Human c-Ha-ras Proto-Oncogene Transgenic Rats in a Medium-Term Bioassay Model for Carcinogens

With the aim of developing a medium-term assay for screening of environmental carcinogens, we exposed mammary carcinogen sensitive human c-Ha-ras proto-oncogene transgenic (Hras128) rats to various carcinogens, including compounds that do not normally induce mammary tumors. Seven-week-old Hras128 rats and wild-type littermates received administrations of 3-methylcholanthrene (3-MC), benzo[a]pyrene (B[a]P), anthracene, pyrene, 2-amino-3-methylimidazo[4,5-f]quinoline (IQ), 2-amino-3,8-dimethylimidazo[4,5-f]quinoxaline (MeIQx), 4-(methyl-nitrosamino)-1-(3-pyridyl)-1-butanone (NNK), dimethylarsinic acid (DMA), diethylnitrosamine (DEN) or azoxymethane (AOM) and were sacrificed at week 12 (females) (at week 10 for the 3-MC group) or week 20 (males). Female Hras128 rats receiving NNK, DEN, or DMA showed a significant increase in mammary tumor incidence and/or multiplicity compared to the respective values with olive oil or deionized distilled water (DDW) vehicles. In male Hras128 rats, a significant increase in mammary tumors was also observed in groups administered 3-MC, B[a]P, anthracene, IQ, and NNK. Mutations of transgenes were observed in codons 12 and/or 61 in the induced tumors by PCR-RFLP except in the DEN group in female and in the MeIQx group in male Hras128 rats. Thus various carcinogens, not necessarily limited to those normally targeting the breast, were found to induce mammary carcinomas in Hras128 rats, especially in females, pointing to potential use for medium-term screening.

Induction of renal and hepatic mixed function oxidases in the hamster and guinea pig

A marked species difference exists in the induction of renal and hepatic mixed function oxidase (MFO) activity between rats and rabbits. However, little is known about MFO induction in these organs from other laboratory animals. Male Golden Syrian hamsters and male Hartley guinea pigs were administered phenobarbital (PB) or beta-napthoflavone (BNF) at 70 and 40 mg/kg, respectively, as daily i.p. injections for 4 days. Polybrominated biphenyl (PBB) (Firemaster BP-6) was given as a single i.p. injection (50 mg/kg). Hamster hepatic microsomal ethoxyresorufin-O-deethylase (EROD) and benzphetamine-N-demethylase (BPND) were selectively induced by BNF and PB, respectively. PBB administration induced both hamster hepatic EROD and BPND. In contrast, hepatic microsomal MFO activity from the guinea pig was inducible by PB, PBB and BNF. Renal microsomal MFO activity in both species was inducible by BNF and PBB as arylhydrocarbon hydroxylase and EROD were induced approximately 10-fold. On the other hand, hamster BPND was induced by PB whereas guinea pig MFO activity was unaffected. Total renal cytochrome P-450 content was not affected by any of these inducers in either species. These data demonstrate selective patterns of induction in both hamster and guinea pig liver and kidney suggesting the involvement of multiple forms of cytochrome P-450.

Polychlorinated biphenyls (PCBs) and polybrominated biphenyls (PBBs): biochemistry, toxicology, and mechanism of action

Polychlorinated and polybrominated biphenyls are industrial chemical mixtures which have been implicated in numerous human poisonings in Taiwan and Japan (PCBs) and Michigan (PBBs). Moreover, these polyhalogenated biphenyls have been widely detected in the environment including the air, water, fish, wildlife, human adipose tissue, and blood and breast milk. A major problem associated with the analysis and toxicology of this group of chemicals is their chemical complexity (e.g., there are 209 possible PCB isomers and congeners) and the remarkable effects of structure on activity. This article will discuss the effects of structure on the biologic and toxic effects of individual PCB and PBB congeners as well as reconstituted mixtures. The results clearly show that like "dioxin" (or 2,3,7,8-TCDD), the PCBs and PBBs elicit their effects through a cytosolic receptor protein which preferentially binds with the toxins which are approximate isostereomers of 2,3,7,8-TCDD. The evidence for this mechanism of action will be discussed in detail.

Species differences in cytochromes P-450 and epoxide hydrolase: comparisons of xenobiotic-induced hepatic microsomal polypeptides in hamsters and rats

Cytochromes P-450 and epoxide hydrolase in hamsters were studied by using two-dimensional gel electrophoresis of hepatic microsomes from untreated animals and those treated with phenobarbital, 3-methylcholanthrene, beta-naphthoflavone, trans-stilbene oxide, and pregnenolone-16 alpha-carbonitrile. Coelectrophoresis with corresponding microsomes from rats and in situ peptide mapping were used to identify resolved microsomal polypeptides as cytochromes P-450 or epoxide hydrolase. Two forms of hepatic microsomal epoxide hydrolase were shown to exist in hamsters; these evidenced extensive structural homology with the corresponding enzyme in rats and were induced by the same xenobiotics. At least eight inducible polypeptides in microsomes from hamsters were tentatively identified as cytochromes P-450. Two of these were electrophoretically identical and structurally related with previously characterized forms of the enzyme in rats. Homologues of several major cytochromes P-450 induced by pregnenolone-16 alpha-carbonitrile and/or phenobarbital in the rat were apparently not present in the hamster. In most cases, putative forms of inducible cytochrome P-450 in the hamster existed at significant levels in microsomes from untreated animals whereas in rats the levels of most inducible forms of the enzyme were low in control microsomes, being more strictly dependent on xenobiotic pretreatment. In contrast with epoxide hydrolase, the molecular complexity of hepatic cytochrome P-450 seems to be comparable for rats and hamsters, but the structure and control of these hemoproteins appear to have markedly diverged.