Modulation by iron of hepatic microsomal and nuclear cytochrome P450, and cytosolic glutathione S-transferase and peroxidase in C57BL/10ScSn mice induced with polychlorinated biphenyls (Aroclor 1254)

Exposure of iron-loaded C57BL/10ScSn mice to the polychlorinated biphenyls (PCBs) mixture Aroclor 1254 in the diet (0.01%) for 5 weeks caused massive hepatic porphyria far greater than occurred with PCBs alone. This regime eventually causes hepatocellular carcinoma. Hepatic microsomal ethoxy-, pentoxy-, and benzyloxyresorufin dealkylase activities (respectively EROD, PROD, and BROD) catalyzed primarily by cytochrome P4501A1 and 2B isoenzymes were markedly induced after 2 weeks of diet (when no porphyria had developed) but showed little effect of iron. EROD activity in the nuclear membrane was also induced by the PCBs as was CYP1A1 protein when shown by immunoblotting. Nuclear dealkylase activities of PCBs-treated mice were considerably less than microsomal activities but were stimulated by iron pretreatment. The mechanism of the iron-enhanced toxicity may be due to oxidative damage associated with chronic induction of CYP1A1 isoforms. Lucigenin-enhanced chemiluminescence (CL) by microsomes and nuclear membranes was used as a method to estimate their potential to form reactive oxygen species. Despite CL being induced by PCBs it was less with microsomes from iron-treated mice. In a comparison of a variety of inducers of microsomal cytochrome P450 there was no correlation between inducer, uroporphyrogenic agent, and intensity of CL. On the other hand, cytosolic glutathione S-transferase (GST) activities with 1-chloro-2,4-dinitrobenzene and 1,2-dichloro-4-nitrobenzene (DCNB) as substrates, were also induced by the PCBs mixture, the induction with DCNB being synergistically potentiated by iron pretreatment. Complementary results were observed by immunocytochemistry using anti alpha-GST antibody. In contrast, total glutathione peroxidase activity and selenium-dependent glutathione peroxidase activity were depressed by PCBs but particularly in mice also administered iron. The results illustrate that PCBs not only induce CYP1A1 in microsomes but also in the nuclear membrane, which may be of significance in the mechanism of the iron-enhanced carcinogenicity of these chemicals. The iron-enhanced induction of GST with accompanying depletion of glutathione peroxidase provides evidence for oxidative processes induced in vivo by the PCBs.

Synergy of iron in the toxicity and carcinogenicity of polychlorinated biphenyls (PCBs) and related chemicals

In Ah-responsive C57BL/10ScSn mice a single dose of iron significantly potentiated the property of the polychlorinated biphenyl (PCB) mixture Aroclor 1254 to induce porphyria by inhibition at the uroporphyrinogen decarboxylase stage of hepatic haem biosynthesis. The induction of liver tumors and other lesions were also enhanced markedly by iron overload suggesting a link between porphyria and cancer. The cellular, molecular and biochemical processes involved have been investigated in attempts to explain these phenomena by an iron-catalysed 'oxidative stress' mechanism.

Perturbation of hepatocyte nuclear populations induced by iron and polychlorinated biphenyls in C57BL/10ScSn mice during carcinogenesis

The induction of hepatocarcinogenesis by polychlorinated biphenyls (PCBs) in C57BL/10ScSn mice is markedly potentiated by iron. To investigate the effects of iron and PCBs on nuclear populations, C57BL/10ScSn mice received a single dose of iron-dextran (600 mg Fe/kg) and were fed a diet containing 0.01% of the PCBs mixture Aroclor 1254 for up to 6 months. DNA content of isolated nuclei and hepatocytes was estimated by flow cytometry. Cell suspensions and nuclei isolated from Aroclor treated mice after 6 months contained increased diploid (2N) populations compared to controls. In contrast, iron treatment of mice markedly enhanced fractions of octoploid (8N) nuclei by 2 weeks and this effect persisted over the 6 month period. When Aroclor 1254 and iron were administered together there was a synergistic increase in the mononucleated diploid fraction which was significant at 2 weeks and highly significant at 6 months. This became the predominant nuclear effect. At six months, Aroclor 1254 and iron, both alone and in combination, also increased the rate of DNA synthesis in hepatocytes as measured by bromodeoxyuridine (BrdU) incorporation. The chronic polyploidizing effect of iron overload alone was investigated further and shown to be proportional to the dose and was detectable as early as 2 days after 600 mg Fe/kg and 1 week after 150 mg Fe/kg. Polyploidization of nuclei was inhibited by the oral iron chelator CP94. Iron also induced a prolonged reduction in the incidence of binucleated cells. Histologically, nuclear enlargement due to iron was confined to the midzonal region of the liver lobule, whereas iron deposition was greatest in the periportal region. Iron (600 mg/kg) also caused increased nuclear polyploid states in hepatocytes of adult rats and gerbils. Similarly, weanling mice with a dominantly diploid cell population, when treated with iron (300 mg/kg), exhibited a significant shift to a tetraploid (4N) population and a marked increase in proliferation as measured by BrdU incorporation and proliferative cell nuclear antigen (PCNA) detection. These results indicate that Aroclor 1254 and iron induce changes in the mouse hepatocyte population that involve 2N and 8N nuclei respectively. The combination treatment leads to the emergence and proliferation of a mononucleated, diploid population as observed frequently in chemical hepato-carcinogenesis. The reason for the chronic polyploidizing effect of iron is unknown, but may imply both increased DNA synthesis and impairment of nuclear division with implications in human conditions of iron overload.

Induction of cytochrome P450 activities by polychlorinated biphenyls in isolated mouse hepatocytes. Influence of Ah-phenotype and iron

Exposure of cultured primary hepatocytes from Ah-responsive male C57BL/10ScSn mice to a polychlorinated biphenyl (PCB) mixture (Aroclor 1254) at 0.1-20 micrograms/mL for up to 96 hr induced cytochrome P4501AI-mediated activity (ethoxyresorufin O-deethylase, EROD) up to 50-fold. In contrast, pentoxyresorufin O-dealkylase (PROD), which in some circumstances is a measure of phenobarbitone-induced cytochrome P450 isoenzymes, was induced only 5-fold. There were similar findings on EROD activities with the pure compounds 3,3',4,4',5,5'-hexachlorobiphenyl, 3,3',4,4',5,5'-hexabromobiphenyl and 3,3',4,4'-tetrachlorobiphenyl(TCB) and also beta-naphthoflavone but not with 2,2',4,4'-TCB or phenobarbitone. The higher concentrations of Aroclor 1254 were also associated with cytotoxicity as estimated by release of alanine aminotransferase (ALT) into the medium. Unlike in C57BL/10ScSn hepatocytes induction of EROD and cytotoxicity was minimal in hepatocytes from the Ah-non-responsive strain DBA/2. Although in vivo the hepatic toxicity and carcinogenicity of polyhalogenated aromatics are markedly potentiated by iron, no enhancement of the cytotoxicity of Aroclor 1254 towards C57BL/10ScSn hepatocytes by iron was observed in vitro. However, iron caused decreased EROD activities and possibly cytochrome P4501AI (as judged by Western blotting) as in vivo. Even in the presence of iron and the haem precursor 5-aminolaevulinic acid (5-ALA) there was no development of uroporphyria in this system although this occurs with Aroclor in vivo and is enhanced by iron. Accumulation of uroporphyrin did occur after extended culture of C57BL/10ScSn hepatocytes on matrigel for 8 days in the presence of 5-ALA and Aroclor 1254 but again no potentiation by iron was observed. Thus, although culture of Ah-responsive and -non-responsive hepatocytes mimics some aspects of the mechanisms of in vivo toxicity of PCBs, there is some unknown associated influence of iron metabolism which cannot, as yet, be produced in vitro but which is of importance in vivo.