On the inhibition of microsomal drug metabolism by polychlorinated biphenyls (PCB) and related phenolic compounds

Environmental polychlorinated biphenyls: acute toxicity of landfill soil extract to female prepubertal rats

Subsurface soil from a National Priorities List landfill containing about 2.5% polychlorinated biphenyls (PCBs) was extracted and the extract cleaned by Florisil slurry and alumina column chromatography. The refined extract contained 48 mg/mL PCB, mainly trichlorobiphenyls and tetrachlorobiphenyls, traces of polychlorinated naphthalenes, 125 micrograms/mL 2,2-bis-p-chlorophenyl-1,1-dichloroethylene (DDE), and low levels of chlorinated dibenzofurans. The refined extract was dissolved in corn oil and administered intraperitoneally to weanling (day 20) female rats on days 20 and 21; rats were terminated on day 22. Limited data indicated possible hematopoietic effects, including neutrophilia. There were no changes in relative uterus, kidney, or adrenal gland weights between total doses of 3 to 96 mg/kg total PCB. Relative liver weights increased significantly at 36 mg/kg and activities of P450s 1A1 (as ethoxyresorufin O-dealkylase) and 2B (as pentoxyresorufin O-dealkylase) increased at 12 mg/kg and plateaued at 36 (P450 1A1) or 48 (P450 2b) mg/kg. Serum total thyroxine (T4) declined significantly at doses of 36 mg/kg and greater; thyroid follicular epithelial cells were significantly larger within the same dose range, but the follicular colloid area decreased to less than 60% control values at 12 mg/kg and remained at this size through 72 mg/kg. Maximum mobilization of T4 apparently occurred at 12 mg/kg and attenuated measured declines in circulating levels. Even though a large proportion of proven and probable estrogenic chlorobiphenyls (CBs) were present, the lower amounts of more potent antiestrogenic aryl hydrocarbon (Ah) receptor agonists and/or decreased responsiveness because of low serum T4 levels may have antagonized the uterotropic response.

Polychlorinated biphenyls (PCBs): environmental impact, biochemical and toxic responses, and implications for risk assessment

Commercial polychlorinated biphenyls (PCBs) and environmental extracts contain complex mixtures of congeners that can be unequivocally identified and quantitated. Some PCB mixtures elicit a spectrum of biochemical and toxic responses in humans and laboratory animals and many of these effects resemble those caused by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and related halogenated aromatic hydrocarbons, which act through the aryl hydrocarbon (Ah)-receptor signal transduction pathway. Structure-activity relationships developed for PCB congeners and metabolites have demonstrated that several structural classes of compounds exhibit diverse biochemical and toxic responses. Structure-toxicity studies suggest that the coplanar PCBs, namely, 3,3',4,4'-tetrachlorobiphenyl (tetraCB), 3,3',4,4',5-pentaCB, 3,3',4,4',5,5'-hexaCB, and their monoortho analogs are Ah-receptor agonists and contribute significantly to the toxicity of the PCB mixtures. Previous studies with TCDD and structurally related compounds have utilized a toxic equivalency factor (TEF) approach for the hazard and risk assessment of polychlorinated dibenzo-p-dioxin (PCDD) and polychlorinated dibenzofuran (PCDF) congeners in which the TCDD or toxic TEQ = sigma([PCDFi x TEFi]n)+sigma([PCDDi x TEFi]n) equivalent (TEQ) of a mixture is related to the TEFs and concentrations of the individual (i) congeners as indicated in the equation (note: n = the number of congeners). Based on the results of quantitative structure-activity studies, the following TEF values have been estimated by making use of the data available for the coplanar and monoortho coplanar PCBs: 3,3',4,4',5-pentaCB, 0.1; 3,3',4,4',5,5'-hexaCB, 0.05; 3,3',4,4'-tetraCB, 0.01; 2,3,3',4,4'-pentaCB, 0.001; 2,3',4,4',5-pentaCB, 0.0001; 2,3,3',4,4',5-hexaCB, 0.0003; 2,3,3',4,4',5'-hexaCB, 0.0003; 2',3,4,4',5-pentaCB, 0.00005; and 2,3,4,4',5-pentaCB, 0.0002. Application of the TEF approach for the risk assessment of PCBs must be used with considerable caution. Analysis of the results of laboratory animal and wildlife studies suggests that the predictive value of TEQs for PCBs may be both species- and response-dependent because both additive and nonadditive (antagonistic) interactions have been observed with PCB mixtures. In the latter case, the TEF approach would significantly overestimate the toxicity of a PCB mixture. Analysis of the rodent carcinogenicity data for Aroclor 1260 using the TEF approach suggests that this response is primarily Ah-receptor-independent. Thus, risk assessment of PCB mixtures that uses cancer as the endpoint cannot solely utilize a TEF approach and requires more quantitative information on the individual congeners contributing to the tumor-promoter activity of PCB mixtures.

The hepatocarcinogenicity of diethylnitrosamine to rainbow trout and its enhancement by Aroclors 1242 and 1254

Rainbow trout (Salmo gairdneri) were fed diets containing 100 ppm Aroclor 1242 (AC42) or Aroclor 1254 (AC54) in combination with 1100 ppm diethylnitrosamine (DEN) for one year. The incidence of hepatocarcinomas was determined and compared with the incidence in trout fed 1100 ppm DEN alone. The two Aroclors dramatically enhanced tumor incidence from 10.2% in the positive controls (DEN alone) to 40.2% for AC42 and 21.6% for AC54. This is in contrast to previous results obtained when AC54 was fed concomitantly with aflatoxin B1 (AFB1), where a substantial inhibition of carcinogenesis was observed. The alteration of chemical carcinogenesis in trout by PCB, therefore, depends upon the carcinogen involved and is not a generalized effect.

Effect of dose on the inhibition of carcinogenesis/mutagenesis by Aroclor 1254 in rainbow trout fed aflatoxin B1

Prior studies have shown that Aroclor 1254 (PCB) differentially alters the incidence of aflatoxin B1 (AFB1) induced hepatocellular carcinomas in trout, depending upon the time of PCB administration relative to AFB1 exposure (Shelton et al., 1983). When fed simultaneously with AFB1, PCB inhibits carcinoma incidence. We investigated the effect of AFB1 and PCB dose on this inhibition. Duplicate tanks of 100 rainbow trout were fed AFB1 at concentrations of 1, 4, or 8 ppb, either with or without the addition of 50 ppm PCB. Other groups were fed 4 ppb AFB1 + 5 ppm PCB, 50 ppm PCB alone, or control diet alone. After 9 and 12 mo, 40 and 60 fish per tank, respectively, were sampled to determine the incidence of liver tumors. The results show a parallel inhibition of the AFB1-tumor dose-response curve by the presence of 50 ppm PCB. Fish fed 4 ppb AFB1 + 5 ppm PCB showed slight inhibition in response when compared with 4ppb AFB1 alone. Also, livers from fish fed 50 ppm PCB were used to prepare S20 for use in the Salmonella mutagenesis assay. These livers were less efficient in converting AFB1 to a mutagen, when compared to control S20. The AFB1-mutagenesis dose-response curve was again shifted parallel to the right of the curve generated using control S20. These results suggest that the inhibitory action is at least partly at the level of carcinogen activation. The finding of parallel, as opposed to proportional, inhibition with varying carcinogen exposure for certain classes of inhibitors may have important implications for inhibition of environmental carcinogenesis at low levels of carcinogen exposure.

Comparison of the effects of acute and subchronic administration of Aroclor 1254, a commercial mixture of polychlorinated biphenyls, on pentobarbital-induced sleep time and [14C]pentobarbital disposition in mice

We have reported previously that polychlorinated biphenyls (PCBs) alter neurochemistry and suppress spontaneous locomotor activity in mice. The present study was initiated to determine whether orally administered (Aroclor 1254) would potentiate pentobarbital-induced sleep time. Sleep time was enhanced significantly by Aroclor 1254 (500 mg/kg) given 0 to 8 h prior to pentobarbital, with the peak effect occurring at 2 h. This effect was demonstrated to be dose-responsive in the range of 5 to 25 mg/kg given 2 h prior to pentobarbital, but only slightly larger increments in sleep time were observed with higher doses of PCBs (50, 100, 250, and 500 mg/kg). Administration of vehicle or Aroclor 1254 (30 or 100 mg/kg) for 14 successive days reduced sleep time when pentobarbital was given 45 min after the last dose of vehicle or Aroclor 1254, with a further reduction when pentobarbital was given 24 h after the last dose. As a correlate to the sleep-time studies, levels of pentobarbital and metabolites were measured in brain, liver, and plasma of mice that had received varying doses of Aroclor 1254 2 h prior to [14C]pentobarbital. Elevated levels of pentobarbital and decreased levels of metabolites were found after acute administration of Aroclor 1254 during a period of time when Aroclor 1254-treated mice were still asleep. These effects of Aroclor 1254 on pentobarbital disposition were found to be dose-dependent. Brain levels of pentobarbital in mice after 14 d of Aroclor 1254 treatment (30 mg/kg) were less than those in vehicle-treated animals, and these levels were consistent with the reduced sleep times. Thus, a correlation between pentobarbital brain levels and sleep time in both Aroclor 1254-treated and nontreated animals suggests that Aroclor 1254 does not alter pentobarbital narcosis by a direct action on the brain. Rather, acutely administered Aroclor 1254 may be augmenting sleep time by competing with pentobarbital for metabolic sites in the liver, while chronically administered Aroclor 1254 induces pentobarbital metabolism.

Effect of trichlorophenols on xenobiotic metabolism in the rat

Unlike halogenated benzenes, trichlorophenols did not induce xenobiotic metabolism in the rat. 2,3,5-, 2,3,6-, 2,4,5-, and 2,4,6-Trichlorophenol at doses as high as 400 mg/kg p.o. daily for 14 days did not alter EPN detoxification. Only 2,4,5-trichlorophenol at the highest dose decreased microsomal NADPH-cytochrome c reductase activity and cytochrome P-450 content. In vitro, all 4 isomers inhibited EPN detoxification and the demethylation of p-nitroanisole. UDP-glucuronyltransferase was not altered in vivo and was only slightly inhibited in vitro by 2,3,5- and 2,4,5-trichlorophenol. The compounds were not hepatotoxic as assessed by measurement of hepatic glucose-6-phosphatase and serum sorbitol dehydrogenase.