Separation of pure polychlorinated biphenyl isomers into two types of inducers on the basis of induction of cytochrome P-450 or P-448

Advanced electrocatalytic redox processes for environmental remediation of halogenated organic water pollutants

Halogenated organic compounds are widespread, and decades of heavy use have resulted in global bioaccumulation and contamination of the environment, including water sources. Here, we introduce the most common halogenated organic water pollutants, their classification by type of halogen (fluorine, chlorine, or bromine), important policies and regulations, main applications, and environmental and human health risks. Remediation techniques are outlined with particular emphasis on carbon-halogen bond strengths. Aqueous advanced redox processes are discussed, highlighting mechanistic details, including electrochemical oxidations and reductions of the water-oxygen system, and thermodynamic potentials, protonation states, and lifetimes of radicals and reactive oxygen species in aqueous electrolytes at different pH conditions. The state of the art of aqueous advanced redox processes for brominated, chlorinated, and fluorinated organic compounds is presented, along with reported mechanisms for aqueous destruction of select PFAS (per- and polyfluoroalkyl substances). Future research directions for aqueous electrocatalytic destruction of organohalogens are identified, emphasizing the crucial need for developing a quantitative mechanistic understanding of degradation pathways, the improvement of analytical detection methods for organohalogens and transient species during advanced redox processes, and the development of new catalysts and processes that are globally scalable.

Aromatic hydrocarbon receptors in mitochondrial biogenesis and function

Mitochondria are ubiquitous membrane-bound organelles that not only play a key role in maintaining cellular energy homeostasis and metabolism but also in signaling and apoptosis. Aryl hydrocarbons receptors (AhRs) are ligand-activated transcription factors that recognize a wide variety of xenobiotics, including polyaromatic hydrocarbons and dioxins, and activate diverse detoxification pathways. These receptors are also activated by natural dietary compounds and endogenous metabolites. In addition, AhRs can modulate the expression of a diverse array of genes related to mitochondrial biogenesis and function. The aim of the present review is to analyze scientific data available on the AhR signaling pathway and its interaction with the intracellular signaling pathways involved in mitochondrial functions, especially those related to cell cycle progression and apoptosis. Various evidence have reported the crosstalk between the AhR signaling pathway and the nuclear factor κB (NF-κB), tyrosine kinase receptor signaling and mitogen-activated protein kinases (MAPKs). The AhR signaling pathway seems to promote cell cycle progression in the absence of exogenous ligands, whereas the presence of exogenous ligands induces cell cycle arrest. However, its effects on apoptosis are controversial since activation or overexpression of AhR has been observed to induce or inhibit apoptosis depending on the cell type. Regarding the mitochondria, although activation by endogenous ligands is related to mitochondrial dysfunction, the effects of endogenous ligands are not well understood but point towards antiapoptotic effects and inducers of mitochondrial biogenesis.

[A memoir of my researches on xenobiotic metabolism for 48 years--researches on Kanemi Yusho and endocrine disrupting chemicals]

The author started a research on xenobiotic metabolism at Graduate School of Pharmaceutical Sciences, Kyushu University in 1965. In 1968, an epidemic of a "strange disease", called Yusho, occurred in western Japan. The epidemic was soon identified to be a food poisoning caused by the ingestion of commercial Kanemi rice bran oil which had been accidentally contaminated with large amounts of polychlorinated biphenyls (PCBs) and their related compounds such as polychlorinated dibenzofurans (PCDFs.) At first, in this review, our toxicological studies on Yusho during the early thirty years were briefly described. Next, the studies on aldehyde oxidase, a molybdenum hydroxylase, which is involved in the lactam formation reaction such as 1-phenyl-2-(2-oxopyrrolidine)pentane(oxoprolintane) from 1-phenyl-2-pyrrolidinopentane(prolintane) and 1-methyl-4-phenyl-1,2,3,6-tetrahydropyridine(MPTP) lactam from 1-methyl-4-phenyl-2,3-dihydropyridinium ion (MPDP⁺) were also presented. Finally, we investigated how the xenobiotic metabolism of endocrine disrupting chemicals such as bisphenol A (BPA) and some isoflavones affects their estrogenic activities. In this study, we demonstrated that BPA is converted to 4-methyl-2,4-bis(4-hydroxyphenyl)pent-1-ene (MBP), an active metabolite as estrogen, by rat liver S9. In the cases of isoflavones, although genistein was inactivated, biochanin A, 4'-methoxy analogue of genistein, was activated to genistein by O-demethylation with rat liver S9.

Regulation of cytochrome P450 expression in Drosophila: Genomic insights

Genomic tools such as the availability of the Drosophila genome sequence, the relative ease of stable transformation, and DNA microarrays have made the fruit fly a powerful model in insecticide toxicology research. We have used transgenic promoter-GFP constructs to document the detailed pattern of induced Cyp6a2 gene expression in larval and adult Drosophila tissues. We also compared various insecticides and xenobiotics for their ability to induce this cytochrome P450 gene, and show that the pattern of Cyp6a2 inducibility is comparable to that of vertebrate CYP2B genes, and different from that of vertebrate CYP1A genes, suggesting a degree of evolutionary conservation for the "phenobarbital-type" induction mechanism. Our results are compared to the increasingly diverse reports on P450 induction that can be gleaned from whole genome or from "detox" microarray experiments in Drosophila. These suggest that only a third of the genomic repertoire of CYP genes is inducible by xenobiotics, and that there are distinct subsets of inducers / induced genes, suggesting multiple xenobiotic transduction mechanisms. A relationship between induction and resistance is not supported by expression data from the literature. The relative abundance of expression data now available is in contrast to the paucity of studies on functional expression of P450 enzymes, and this remains a challenge for our understanding of the toxicokinetic aspects of insecticide action.

Interaction of polyhalogenated compounds of appropriate configuration with mammalian or bacterial CYP enzymes. Increased bilirubin and uroporphyrinogen oxidation in vitro

Polyhalogenated compounds, such as 2,3,7,8-tetrachlorodibenzo-p-dioxin, are associated with toxic Uroporphyria and cause alleviation of jaundice in the Gunn rat. These effects have been attributed to a microsomal oxidation of uroporphyrinogen and bilirubin for which supportive evidence has been obtained in vitro. CYP1A1 required planar polyhalogenated biphenyls for these oxidative reactions, while CYP1A2 was capable of oxidation in their absence. We have now used rat CYP1A1 and confirmed with the pure enzyme that increased bilirubin oxidation was caused by the addition of 3,4,3',4'-tetrachlorobiphenyl. CYP1A2 was more active than CYP1A1 at oxidizing bilirubin in presence of NADPH alone and reacted to addition of 3,4,3',4'-tetrachlorobiphenyl with a depression rather than a stimulation of bilirubin oxidation. We have also tested a bacterial enzyme, CYP102. Dodecanoic acid and its polyhalogenated analogue (perfluorododecanoic acid) both stimulated NADPH oxidation by CYP102, but only the perfluoro analogue stimulated markedly bilirubin oxidation. The analogue exhibited much greater potency than the normal substrate in stimulating NADPH and bilirubin oxidation and also showed greater affinity for CYP102, as measured by the binding constant, Ks. The molar stoichiometry ratio between NADPH and O(2) consumption was 1 in the case of the substrate, but approximated 2 with the perfluoro analogue. We conclude that halogenated substrate analogues can interact with different CYPs to increase production of oxidative species, probably by an uncoupling mechanism. A role of the ferryl-oxygen intermediate is suggested in the oxidation of biologically important molecules, with possible implications for the therapy of jaundice and for toxic oxidative reactions, such as uroporphyria and cancer.

Aryl hydrocarbon receptors: diversity and evolution

Animals have evolved inducible enzymatic defenses to facilitate the biotransformation and elimination of toxic compounds encountered in the environment. The sensory component of this system consists of soluble receptors that regulate the expression of certain isoforms of cytochrome P450, other enzymes, and transporters in response to environmental chemicals. These receptors include several members of the steroid/nuclear receptor superfamily as well as the aryl hydrocarbon receptor (AHR), a member of the bHLH-PAS gene superfamily. In addition to its adaptive functions, the AHR serves poorly understood physiological roles; interference with those roles by dioxins and related chemicals causes toxicity. One approach to understanding the physiological significance of the AHR is to characterize its structure, function, and regulation in diverse species, including mammals, birds, fish, and invertebrates. These animal groups include model species with unique features that can be exploited to broaden our understanding of AHR function. Studies carried out in diverse species also provide phylogenetic information that allows inferences about the evolutionary history of the AHR. This review summarizes the current understanding of AHR diversity among animal species and the evolution of the AHR signaling pathway, as inferred from molecular studies in vertebrate and invertebrate animals. The AHR gene has undergone duplication and diversification in vertebrate animals, resulting in at least three members of an AHR gene family: AHR1, AHR2, and AHR repressor. The inability of invertebrate AHR homologs to bind dioxins and related chemicals, along with other evidence, suggests that the adaptive role of the AHR as a regulator of xenobiotic metabolizing enzymes may have been a vertebrate innovation. The physiological functions of the AHR during development appear to be ancestral to the adaptive functions. Sensitivity to the developmental toxicity of dioxins and related chemicals may have had its origin in the evolution of dioxin-binding capacity of the AHR in the vertebrate lineage.

Bilirubin and uroporphyrinogen oxidation by induced cytochrome P4501A and cytochrome P4502B. Role of polyhalogenated biphenyls of different configuration

In previous work it was shown that hepatic microsomes from rats treated with 3-methylcholanthrene and similar inducers had increased bilirubin-degrading activity. The activity was further stimulated by addition of 3,4-tetrachlorobiphenyl (TCB), a response specifically dependent on CYP1A1. Here, we compared the effect of adding PCBs of either planar or non-planar configuration on rate of bilirubin degradation, monooxygenase activity and NADPH/O(2) consumption by liver microsomes from animals treated with either phenobarbital or 3-methylcholanthrene/beta-naphthoflavone. We also examined the oxidation of uroporphyrinogen (hexahydro-uroporphyrin) (URO'gen) under these conditions. Polychlorinated biphenyl (PCBs) stimulated the rate of bilirubin and URO'gen oxidation with microsomes expressing high levels of either CYP2B or CYP1A, inhibiting at the same time their monooxygenase activities (PROD and EROD, respectively); however, non-planar di-ortho-substituted PCBs were preferentially active with phenobarbitone-induced microsomes, in contrast to those active with 3-methylcholanthrene/beta-naphthoflavone microsomes, where a planar configuration was required for activity. An antibody raised against CYP2B1 markedly inhibited the PCB-dependent bilirubin degradation and PROD activities of phenobarbital-induced microsomes with similar dose-response curves for the two effects. Increased microsomal utilizations of NADPH and O(2) were also caused by PCBs with both types of induced microsomes and here again PCBs of different configuration were preferentially active. It is concluded that PCBs of the appropriate configuration may interact with either CYP1A1 or CYP2B1, increase production of oxidative species by an uncoupling mechanism, and lead to oxidation of target molecules in the cell, among these uroporphyrinogen and bilirubin.

Polychlorinated biphenyls, polychlorinated dibenzo-p-dioxins, and polychlorinated dibenzofurans as endocrine disrupters--what we have learned from Yusho disease

Polychlorinated biphenyls (PCBs), polychlorinated dibenzo-p-dioxins, and polychlorinated dibenzofurans (PCDFs) are persistent environmental pollutants. In some areas wildlife reproduction has been affected by these compounds, which are recognized as endocrine disrupters. In 1968 in northern Kyushu in Japan about 2000 people were poisoned by PCBs and PCDFs (pyrolysis products of PCBs) which contaminated rice oil. Their condition was named "Yusho" disease. A similar poisoning by PCBs in Taiwan was named "Yu-Cheng" disease. The major symptoms of Yusho disease were dermal and ocular lesions, but some of the symptoms, such as irregular menstrual cycles and altered immune responses, were notable with respect to the endocrine disrupting activities of PCBs and related compounds. Several important observations relevant to the mechanisms of Yusho have been made from animal studies. For example, a coplanar PCB congener was shown to cause atrophy of the thymus and PCB administration was thought to alter androgen metabolism. The most tragic aspect of Yusho and Yu-Cheng diseases was the exposure of children to PCBs. In the case of Yu-Cheng, children exposed to PCBs in utero and lactationally were reported to have poor cognitive development. Intellectual impairment was also observed in children born to women who had eaten fish contaminated with PCBs in the United States. From animal studies, alterations in thyroid hormone status, modulation of protein kinase C, and changes in dopamine levels, etc. were proposed as the possible mechanisms for the adverse effects of PCBs on brain development. Whereas coplanar PCB and related congeners, e.g., 2,3,7,8-tetrachlorodibenzo-p-dioxin, induce gene expression via a ligand-dependent transactivating factor, the arylhydrocarbon receptor, alternative pathways for gene expression, e.g., c-Src and cross talk with the MAP kinase pathway, are also reviewed with respect to understanding the toxic mechanisms of these compounds. Finally, the "precautionary principle" is discussed for prevention of the health hazards caused by exposure to endocrine disrupters.

Dioxin-like and non-dioxin-like toxic effects of polychlorinated biphenyls (PCBs): implications for risk assessment

Polychlorinated biphenyls (PCBs) are persistent, bioaccumulative, and toxic contaminants in the environment. Individual PCB congeners exhibit different physicochemical properties and biological activities that result in different environmental distributions and toxicity profiles. The variable composition of PCB residues in environmental matrices and their different mechanisms of toxicity complicate the development of scientifically based regulations for the risk assessment. In this article various approaches for the assessment of risks of PCBs have been critically examined. Recent developments in the toxic equivalency factor (TEF) approach for the assessment of toxic effects due to dioxin-like PCBs have been examined. PCB exposure studies that describe non-dioxin-like toxic effects, particularly neurobehavioral effects and their effective doses in animals were compiled. A comparative assessment of effective doses for dioxin-like and non-dioxin-like effects by PCBs has been made to evaluate the relative significance of non-ortho-and ortho-substituted PCBs in risk assessment. Using mink as an example, relative merits and implications of using TEF and total PCB approaches for assessing the potential for toxic effects in wildlife was examined. There are several advantages and limitations associated with each method used for PCB risk assessment. Toxic effects due to coplanar PCBs occur at relatively smaller concentrations than those due to non-dioxin-like PCBs and therefore the TEF approach derives the risk assessment of PCBs, in the environment. The need for the refinement of TEF approach for more accurate assessment of risks is discussed.

Microsomal enzyme activity, glutathione S-transferase-placental form expression, cell proliferation, and vitamin A stores in livers of rats consuming Great Lakes salmon

Male and female Sprague-Dawley rats were fed diets incorporating lyophilized chinook salmon obtained from Lake Ontario and Lake Huron. After 70 days, females were bred and the progeny (F1) were reared on the same fish-based diets as the adults (F0). After 78-133 days on the diets, males and females of both generations were sacrificed and hepatic microsomal enzyme activities determined, along with glutathione S-transferase-placental form (GSTP) expression and hepatic cellular proliferation. Hepatic P450 enzyme activities (MROD, EROD, PROD, BROD, and aminopyrine) were increased significantly by fish diets from both sources. Increases in hepatic enzyme activity were greatest for fish caught from Lake Ontario and reflected the total levels of organochlorine contaminants in the fish. GSTP and cell proliferation rates did not show any diet-related or dose-related changes. Vitamin A stores were analyzed as the concentration of liver retinyl palmitate. In rats receiving the highest TEQ dose (i.e., 20% Lake Ontario fish diet), vitamin A stores were significantly lower in F0 adults, F1 weanlings, and F1 adult females.

Structure-dependent induction of CYP2B by polychlorinated biphenyl congeners in female Sprague-Dawley rats

The dose-response induction of hepatic microsomal pentoxyresorufin O-dealkylase (PROD) activity by phenobarbital (PB) and several polychlorinated biphenyl (PCB) mixtures and congeners was determined in the immature female Sprague-Dawley rat. At a dose of 75 mg/kg/day of PB for 3 days, the microsomal PROD activity was 2154 pmol/min/mg protein. Aroclors 1260, 1254, 1242, and 1016 did not induce maximal PROD activity at doses up to 500 mg/kg, and only Aroclor 1016 induced > a half-maximal response at the 500 mg/kg dose. The relative potencies of eighteen different PCB congeners were also determined, and the structures of these compounds differed with respect to the degree of chlorination (tri- to octochloro) and substitution patterns. The relative potencies of these compounds were estimated by comparing their induced activities at the high dose (150 or 100 mg/kg) with that of PB. The most potent inducers were 2,3,3',4',5,6-hexaCB and 2,2',3,4',5,5',6-heptaCB; at a dose of 150 mg/kg, the PROD activity induced by 2,2'3,4',5,5',6-heptaCB was comparable to that observed for PB. 2,3,3',4',5,6-HexaCB was the most potent inducer, and hepatic PROD activity in rats treated with 150 mg/kg was 4202 pmol/min/mg; this value was higher than that observed for PB at a dose of 75 mg/kg. A second group of congeners including 2,2',3,4,4',5,5'-heptaCB, 2,2',4,4',5,5'-hexaCB, 2,2',3,3',4,4',5,5'-octaCB 2,2',4,4'-tetraCB, 2,2',4,5,5'-pentaCB, 2,2',3,4,4',5',6-heptaCB, 2,2',4,4',5-pentaCB and 2,2',3,3',4',5,5',6-octaCB induced PROD activity > or = 1090 pmol/min/mg at the 150 mg/kg dose, and this value was > 50% of the maximal response observed for PB. The remaining compounds, namely 2,4,4'-triCB, 2,2',3,4'-tetraCB, 2,2',5,5'-tetraCB, 2,3',4,4',5-pentaCB, 2,3,3',4,4'-pentaCB, 2,2',4,4',5,6'-hexaCB, 2,3,3',4,4',5,5'-heptaCB and 2,2',3,3',4,4,5-heptaCB were all relatively weak inducers of hepatic microsomal PROD activity ( < 450 pmol/min/mg). In parallel experiments, western blot analysis of immunoreactive CYP2B1 and CYP2B2 protein showed that PB, the PCB mixtures, and congeners induced both proteins. Previous studies have identified a cis-acting DNA element that plays a role in regulating CYP2B1/B2 gene expression and binds nuclear trans-acting factor(s) induced by PB. The results of gel electrophoretic mobility shift assays with nuclear extracts showed that both PB and 2,2',3,4',5,5',6-heptaCB induce formation of a common retarded band using a 32P-labeled oligonucleotide corresponding the the cis-acting DNA promoter sequence. Both PB and PCBs appear to induce CYP2B1/B2 via a common mechanism. Although the results of this study do not define structure-induction (CYP2B1/B2) relationships for PCBs, two compounds, namely 2,3,3',4',5,6-hexaCB and 2,2',3,4',5,5',6-heptaCB, were identified as highly potent inducers.

Induction of cytochrome P-450 in the Norway rat, Rattus norvegicus, following exposure to potential environmental contaminants

Cytochrome P-450 (CYP) induction (consisting of increases in cellular RNA and protein content and associated catalytic activities) occurs predominantly in the liver, but also in small intestine, lung, kidney, and placenta, of Norway rats (Rattus norvegicus) exposed to certain types of potential environmental contaminants. The specific isoform(s) induced in the rat and the magnitudes of the increases observed depend upon the chemical nature of the xenobiotic. For instance, the predominant isoforms induced by nonhalogenated polycyclic aromatic hydrocarbons, such as petroleum derivatives and coal-tar constituents such as the benzopyrenes and the anthracenes, are those of the CYP1A subfamily. Polyhalogenated aromatic hydrocarbons, such as the halogenated dibenzodioxins, dibenzofurans, and biphenyls, may cause the induction of predominantly the CYP1A subfamily, predominantly the CYP2B subfamily, or mixed CYP1A- and CYP2B-type induction, depending upon the halogen substitution pattern. In contrast, the chlorinated hydrocarbon pesticides, such as DDT, dieldrin, chlordane, and mirex, cause almost exclusively the induction of isoforms of the CYP2B (and to a lesser extent the CYP3A) subfamilies. The commonly employed plasticizing agent di-(2-ethylhexyl)phthalate elicits predominantly induction of the CYP4A subfamily. Those xenobiotics that would be expected to be the most pervasive environmental contaminants are typically those that have also been found to cause the most profound CYP induction responses. Such chemicals are extremely lipophilic and tend to accumulate in animal tissues, especially fatty tissues such as the liver. The hepatic CYP induction response to such potential environmental contaminants is typical of the animals' response to lipophilic xenobiotics in general, and serves as a mechanism by which the excretion of such compounds from the body is facilitated.

Isomer-specific analysis of polychlorinated biphenyls and 2,3,7,8-tetrachlorodibenzo-p-dioxin equivalents (TEQs) in red fox and human adipose tissue from central Italy

The general exposure of humans and foxes to polychlorinated biphenyls (PCBs) and DDT in Italy was determined by analysis of adipose tissue samples collected from 1991-1992. sigma PCB concentrations varied between 1.0 and 2.6 micrograms/g (wet wt.). sigma DDT concentrations ranged from 1.6 to 5.0 micrograms/g (wet wt.). About thirty-five PCB congeners were identified in most samples. PCB congeners of IUPAC Nos. 138, 153, and 180 were the most abundant compounds, accounting for an average of 50% of the sigma PCBs in humans and 64% in foxes. Generally, higher chlorinated biphenyls and those with a 2,4,5-chlorine substitution in one ring and at least one substitution in the 4-position of the other ring were preferentially accumulated. Coplanar PCB congeners were detected at considerable concentrations and there is no sign of decline in their concentrations with respect to previously reported data. IUPAC Nos. 118, 156 and 126 were the main contributors to toxicity in humans and foxes. The significant contribution of mono-ortho congeners in humans and non-ortho congeners in foxes suggests that differences in metabolic potential may affect the PCB toxicity pattern.

Urinary ascorbic acid--HPLC determination and application as a noninvasive biomarker of hepatic response

A high-performance liquid chromatograph (HPLC) procedure has been developed for the determination of rat urinary ascorbic acid, a major metabolite of the hepatic glucuronic acid pathway. The presence of EDTA and HCl effectively inhibited degradation of ascorbic acid during the collection of urine specimens. The reliability of the procedure was demonstrated by its high recovery (90%), specificity (characteristic absorption maximum and discrimination from isoascorbic acid), and reproducibility (2-3% coefficient of variation). The usefulness of this assay as an indicator of hepatic response was demonstrated in preliminary experiments where increases in urinary ascorbic acid excretion were detected in male rats treated with PCB 126 (3,3',4,4',5-pentachlorobiphenyl) or PCB 105 (2,3,3',4,4'-pentachlorobiphenyl). The HPLC measurement also showed that the two PCB congeners differed markedly in their potency in stimulating urinary ascorbic acid excretion. For example, 10 micrograms/kg bw/day of PCB 126 was sufficient to cause a fourfold increase in urinary ascorbic excretion while 5000 micrograms/kg bw/day of PCB 105 was required for a sevenfold increase. In response to the administration of PCB 105 or PCB 126, urinary ascorbic acid appeared to increase to the same extent as increases in hepatic ethoxyresorufin O-deethylase (EROD) and UDP-glucuronosyltransferase (UGT) activities, and to a much higher extent than changes in liver weight and hematological and serum clinical chemical parameters. The sensitivity and specificity, the ease in obtaining timed specimens, and the noninvasive nature make this assay a useful biomarker of hepatic response in dose-finding and various acute and chronic studies.

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.

Repeated exposure to the polychlorinated biphenyl (Aroclor 1254) elevates the basal serum levels of corticosterone but does not affect the stress-induced rise

Previous studies indicate that repeated exposure of weanling male Fischer 344 rats to Aroclor can cause immune system alterations but the pattern of effects suggested the release of corticosteroids may have played a role. Rats were exposed daily by gastric intubation to the polychlorinated biphenyl (PCB) Aroclor 1254 at 0.1, 1.0, 10, or 25 mg/kg for exposure durations of 5, 10 or 15 weeks. By the 15th week of dosing all groups displayed an elevation in the basal level of serum corticosterone but no change in adrenal weight. Further, rats exposed to Aroclor 1254 for 15 weeks and subjected to stress prior to serum collection displayed elevations in corticosterone levels equivalent to stressed control rats. The failure to observe altered adrenal structure indicative of hyperactivity in the presence of increased serum levels of corticosterone suggest these basal increases may be indirect rather than direct effects of Aroclor 1254.

Relative tumour promoting activity of three polychlorinated biphenyls in rat liver

The relative tumour promoting activity of three structurally and toxicologically diverse polychlorinated biphenyls (3,4,5,3',4'-penta- 2,3,4,3',4'-penta- and 2,4,5,2',4',5'-hexachlorobiphenyl) was measured in an initiation/promotion assay in nitrosodiethylamine-initiated female Sprague-Dawley rats. The congeners under study were administered by once-weekly subcutaneous injections for 20 weeks. Evaluation of the development of gamma-glutamyl transpeptidase (GGT)- and glutation transferase P (GST-P)-positive hepatic foci showed that all congeners promoted altered hepatic foci, although 3,4,5,3',4'-pentachlorobiphenyl was far more potent. The volume fraction of the liver occupied by GGT-positive tissue in the 3,4,5,3',4'-pentachlorobiphenyl-treated animals (100 micrograms/kg per week) was 23%, while the volume fractions of altered liver tissue in the rats treated with 2,3,4,3',4'-pentachlorobiphenyl (5000 micrograms/kg per week) and 2,4,5,2',4',5'-hexaCB (20,000 micrograms/kg per week) were 1.2 and 2.3, respectively. The enhancement of GGT- and GST-P-positive foci was accompanied by an increased incidence of histological changes in the livers.

Polychlorinated biphenyl residues in food and human milk: determination of co-planar and mono-ortho substituted congeners

An analytical method is described for determining the residues of coplanar as well as mono-ortho substituted PCB congeners both exhibiting toxicological relevance, in foods of animal origin and in human milk. The unsophisticated procedure, convenient for routine analyses, includes the extraction of lipids, clean-up steps using liquid/liquid partition and column chromatography, fractionation of the congeners using HPLC on a special carbon column with an optimal gradient elution, and capillary column gas chromatography with electron capture or mass spectrometric detection. As preliminary results indicate, the low-chlorinated PCB technical products contribute more to the actual contamination of environment and foods than has been estimated so far. Obviously the co-planar congeners are accumulated during the food chain in a portion different from that found for the other congeners.

Simultaneous determination of planar chlorobiphenyls and polychlorinated dibenzo-p-dioxins and -furans in Dutch milk using isotope dilution and gas chromatography-high-resolution mass spectrometry

A method is described for the simultaneous determination of planar chlorobiphenyls and dioxins in milk using isotope dilution and gas chromatography-high-resolution mass spectrometry (GC-MS). The method is based on gel permeation chromatography, alumina clean-up and carbon chromatography and is highly automated, making a high sample throughput possible. Data on recovery, accuracy and reproducibility of results obtained with quality control samples are presented. Data for both dioxins and planar chlorobiphenyls from the analysis of samples of Dutch milk from several areas in the Netherlands are also presented. Possible interference of the chlorobiphenyls in the determination of the dioxins in the GC-MS method is discussed.

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.

Elimination of PCB congeners via milk in rabbits administered Fenclor 64

A single dose of 100 mg per kg body weight of a commercial mixture of polychlorinated biphenyls (PCB), Fenclor 64 was given intraperitoneally to pregnant rabbits. The distribution in dams and foetuses and excretion in milk was investigated for six of the congeners by quantifying them in fat from maternal adipose tissue, from whole foetuses and newborn bodies and from newborn gastric contents. The cytochrome-P-450 induction after Fenclor 64 in foetuses and suckling off-spring was followed by measuring the following hepatic mixed function oxidase (MFO) activities: p-nitroanisole-demethylase, ethoxyresorufin-deethylase, ethoxycoumarin-deethylase and NADPH cytochrome-C reductase. At the 28th day of pregnancy PCB fat concentrations in foetuses were similar to those in mothers (126.4 +/- 7.1 and 152.6 +/- 28.1 micrograms/g of fat, respectively). By the 5th day of life fat concentrations in the youngs were double those of foetuses (216.81 +/- 8.12 micrograms/g) and remained high until weaning (142.2 +/- 15.5 micrograms/g at the 20th day). PCB concentrations in mothers' fat decreased during lactation (104.1 micrograms/g at the 20th day) but at the end of the experiment they were still high (95.5 micrograms/g). The cytochrome-P-450 concentration and MFO activities in young rabbits' livers from treated dams were significantly higher than controls from the 5th (P less than 0.01) to the 10th (P less than 0.01) day of life, with the exception of NADPH-cyt-C-reductase (P less than 0.05).(ABSTRACT TRUNCATED AT 250 WORDS)

Inhibition of dye transfer in rat liver WB cell culture by polychlorinated biphenyls

In the present investigation the scrape loading/dye transfer assay and microinjection technique are used in order to investigate inhibition of cell-cell communication induced by different polychlorinated biphenyl (PCB) congeners. In these in vitro assays, inhibition of intercellular communication is directly measured as decreased transfer of a fluorescent dye (Lucifer Yellow CH) from donor cells loaded with the dye to surrounding recipient cells. The results show that substitution in the ortho position from the carbon bridge is essential and at least one chloro substituent in ortho position is necessary for the ability to inhibit intercellular communication. The results also suggest that an increase in the number of ortho substituted chlorine atoms in the PCB molecule enhances the ability to inhibit intercellular communication. On the other hand, the total number of substitutions may not be crucial for the ability to inhibit intercellular communication. Our results suggest that PCB-induced down-regulation of intercellular communication is a result of a specific mechanism and not due to unspecific membrane perturbation.

Aminopyrine-N-demethylase. I. Directed modification of substrates' structure as a way of production of inducer of the monooxygenase isoform P-450b

The effect of the phenobarbital-type monooxygenase inducers is accomplished via the native molecule. This made it possible to transform the typical substrate of cytochrome P-450b aminopyrine into an inducer of this isozyme by blocking the substrate molecule position undergoing monooxygenation. Substitution of two methyl groups in the aminopyrine -N(CH3)2 position by an isopropyl group gave rise to a clear-cut inducive effect. This was registered by spectral, kinetic, radiological and immunochemical methods.

Differential induction of cytochromes P450 and cytochrome P450-dependent arachidonic acid metabolism by 3,4,5,3',4'-pentachlorobiphenyl in the rat and the guinea pig

Differential induction of hepatic cytochromes P450 by 3,4,5,3',4'-pentachlorobiphenyl (PENCB) has been observed in the rat and the guinea pig: (1) in rat and guinea pig, treatment with the chosen dose levels resulted in significant induction of total, carbon monoxide-discernible cytochrome P450 content; the absorption maximum of the CO-adduct of the dithionite-reduced microsomes from PENCB-induced rat liver was shifted from 450 to 448 nm, whereas its counterpart in the guinea pig did not; (2) PENCB treatment significantly increased EROD activity in rat liver microsomes (up to 60-fold), but the increase in the guinea pig was less than fivefold; (3) PENCB-induced rat liver microsomes significantly induced the omega-1 hydroxylation of arachidonic acid (AA); however, omega-1 hydroxylation of AA was hardly affected by PENCB treatment in the guinea pig. Instead, omega-hydroxylation was significantly increased in this latter species. In addition to omega-1 hydroxylation in the rat or omega-hydroxylation in the guinea pig, an additional AA metabolite (designated peak III) was significantly induced by PENCB in both rat and guinea pig; (4) Western blot and ELISA analyses with polyclonal anti-P450 IA1/IA2 and IVA1 antibodies demonstrated that P450 IA1 was significantly induced in the rat but only slightly induced in the guinea pig, whereas P450 IVA1 was significantly suppressed in the rat but significantly induced in the guinea pig by PENCB treatment. The induction of the third arachidonic acid metabolite peak, Peak III, in both rat and guinea pig, particularly in the guinea pig, is obviously neither mediated by P450 IA1 nor by P450 IV A1. At present, it is still unclear which form(s) of cytochrome P450 isoenzymes is responsible for this latter hydroxylation of arachidonic acid.

Differential potency of atropisomers of polychlorinated biphenyls on cytochrome P450 induction and uroporphyrin accumulation in the chick embryo hepatocyte culture

The atropisomers of 2,2',3,4,6-pentachlorobiphenyl (PeCB), 2,2',3,4,4',6-hexachlorobiphenyl (HeCB), and 2,2',3,3',4,4',6,6'-octachlorobiphenyl (OCB) were studied in the chick embryo hepatocyte culture to determine if chirality plays a role in the recognition events associated with the induction of cytochromes P450 and the accumulation of uroporphyrin (URO). Concentration-related induction of cytochrome P450 content, ethoxyresorufin-O-deethylase (EROD) and benzphetamine N-demethylase (BPDM) activities were measured. The rank order of potency for total cytochrome P450 induction was HeCB greater than OCB greater than or equal to PeCB. The (+)- and (-)-enantiomers of PeCB and OCB were of equal potencies as inducers of cytochromes P450, whereas the (+)-HeCB was greater than the (-)-HeCB. HeCB was a much more potent inducer of EROD activity than was either PeCB or OCB. EROD activity was induced to a much greater extent by the (+)-enantiomers of all compounds, with the (-)-enantiomers of PeCB and OCB being inactive. BPDM activity was induced by all three compounds in the order of OCB greater than or equal to HeCB greater than PeCB. The (-)-enantiomers were more potent inducers of BPDM activities than were the (+)-enantiomers, except for HeCB, in which the (+)- was more potent than the (-)-enantiomer. Analysis of porphyrin accumulation in cultures treated with delta-aminolevulinic acid revealed that (+)-HeCB caused the greatest percent URO accumulation, which also correlated with the greatest increase in EROD activity. All other enantiomers caused up to 47% URO accumulation, which did not correlate with an increase in EROD activity.

Induction of hepatic cytochrome P-450IA1 in pigeons treated in vivo with Aroclor 1254, a commercial mixture of polychlorinated biphenyls (PCBs)

1. Treatment with a commercial mixture of polychlorinated biphenyls (PCBs) resulted in highly significant increases in pigeon hepatic microsomal proteins (100-fold), cytochrome P-450 (11-fold), cytochrome b5 (7-fold), NADPH-cytochrome c-(P450) reductase (7-fold), ethoxycoumarin-O-deethylation (9-fold), aldrin epoxidase (22-fold), ethoxyresorufin-O-deethylation (48-fold), N-demethylation of dimethylnitrosamine (28-fold) but not of lauric acid 12-hydroxylation. 2. SDS-PAGE analysis of pigeon hepatic microsomal proteins induced by Aroclor 1254 suggested highly significant increases in the density of staining in bands of estimated Mr 51-52 kD, 54-54.5 kD, 57-58 kD, 59-60 kD and of 77.5-78.5 kD. 3. The induction of cytochrome P-450IA1 was confirmed by Western immunoblotting using the monoclonal antibodies MAB 1-12-3 and MAB 1-8-4. 4. There was agreement between the 8-fold increase in cytochrome P-450IA1 increased staining of microsomal proteins, as judged by SDS-PAGE, and the 24-fold increase in the amount of protein that reacted with the monoclonal antibodies MAB 1-12-3 and MAB 1-8-4, as judged by Western immunoblotting. 5. It is concluded that treatment with a commercial PCB mixture resulted in the induction of several isoforms of pigeon hepatic cytochrome P-450 in a fashion that is likely to be similar to that reported for mammals.

Comparison of polychlorinated dibenzodioxin levels with hepatic mixed-function oxidase induction in great blue herons

As part of the Canadian Wildlife Service monitoring of great blue herons in British Columbia, eggs were collected from three colonies with low, intermediate, and high levels of PCDD and PCDF contamination: Nicomekl, Vancouver, and Crofton, respectively. One egg from each nest was used for chemical analysis by GC-MS; the others were hatched. Liver microsomes were prepared from the heron chicks and used for determination of cytochrome P-450-dependent activities. No erythromycin N-demethylase activity was found in any sample. Ethoxyresorufin O-dealkylase activity in the Nicomekl group was similar to that in pigeons, a control altricial species. The ethoxyresorufin activity in the herons from the Crofton colony was 2.6-fold higher than in the Nicomekl group. The Vancouver colony was intermediate. No difference among the three heron colonies was found in pentoxyresorufin O-dealkylase activity, although levels were 20-33 times that in the pigeon. Chemical analysis was carried out on paired heron eggs. Vancouver and Crofton eggs contained 13.5 and 21 times the levels of 2,3,7,8-TCDD compared to the Nicomekl group. The Crofton eggs contained higher levels of several other contaminants also. A highly significant correlation (p less than .001) was found between ethoxyresorufin O-dealkylase and 2,3,7,8-TCDD concentrations. The correlation coefficient did not change when ethoxyresorufin O-dealkylase was compared to total chemical contamination using several toxic equivalency factors. Multiple regression analysis resulted in only one predictor variable for ethoxyresorufin O-dealkylase: 2,3,7,8-TCDD.

Selective induction of cytochrome P450 isozymes in rat liver by 4-n-alkyl-methylenedioxybenzenes

To examine the structural requirements of cytochrome P450 induction by 4-n-alkyl-substituted methylenedioxybenzenes (MDBs), rats were treated in vivo with a series of MDBs that differed in alkyl carbon side-chain length (0, 1, 2, 3, 4, 5, 6, or 8). Expression patterns of specific P450 isozymes were evaluated with Western and Northern blotting, enzymatic assays, and solution hybridization assays. As determined by carbon monoxide difference spectroscopy, maximal hepatic induction of total P450 content occurred when rats were treated with MDB derivatives with alkyl chain lengths of five or six carbons. However, maximum induction of the specific P450s--P450IA1, P450IIB1, and P450IIB2--occurred with n-hexyl-MDB. In contrast to effects observed with phenobarbital, treatment with MDBs resulted in higher levels of P450IIB2 than of P450IIB1 in rat hepatic microsomes. Western blot quantitation of MDB-induced hepatic P450IIB1 and P450IIB2 apoenzymes did not correlate to measured levels of the corresponding P450 mRNAs. In fact, P450IIB1 and P450IIB2 apoenzyme levels were consistently lower than expected based on Northern blot and solution hybridization measures of the respective mRNAs. These data suggest that the n-alkyl-MDBs effect increases in levels of hepatic P450 in a complex manner, producing accumulation of P450 mRNAs concomitant with alterations in processes regulating steady-state levels of P450 apoenzyme.

Polychlorinated biphenyls (PCBs), dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and related compounds: environmental and mechanistic considerations which support the development of toxic equivalency factors (TEFs)

Halogenated aromatic compounds, typified by the polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), biphenyls (PCBs), and diphenylethers (PCDEs), are industrial compounds or byproducts which have been widely identified in the environment and in chemical-waste dumpsites. Halogenated aromatics are invariably present in diverse analytes as highly complex mixtures of isomers and congeners and this complicates the hazard and risk assessment of these compounds. Several studies have confirmed the common receptor-mediated mechanism of action of toxic halogenated aromatics and this has resulted in the development of structure-activity relationships for this class of chemicals. The most toxic halogenated aromatic is 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and based on in vivo and in vitro studies the relative toxicities of individual halogenated aromatics have been determined relative to TCDD (i.e., toxic equivalents). The derived toxic equivalents can be used for hazard and risk assessment of halogenated aromatic mixtures; moreover, for more complex mixtures containing congeners for which no standards are available (e.g., bromo/chloro mixtures), several in vitro or in vivo assays can be utilized for hazard or risk assessment.

The pharmacokinetics of 2,2',5,5'-tetrachlorobiphenyl and 3,3',4,4'-tetrachlorobiphenyl and its relationship to toxicity

The pharmacokinetics of two toxicologically diverse tetrachlorobiphenyls (TCBs) were measured in mice. After dosing to apparent steady-state conditions, 2,2',5,5'-TCB was found to have a tissue elimination half-life of between 1.64 and 2.90 days. The half-life of 3,3',4,4'-TCB was similar, ranging from 1.07 to 2.60 days. Systemic clearance and volume of distribution estimates were also similar for the two TCB isomers. The 3,3',4,4'-isomer had a substantially greater partitioning from serum into adipose, liver, and thymic tissues. With dosing regimens developed using these measured pharmacokinetic parameters, experiments were undertaken to compare toxic potency of these two TCBs when similar tissue concentrations of the two isomers were achieved in target and storage tissues. These studies demonstrated that thymic atrophy occurs at lower 3,3',4,4'-TCB doses and tissue concentrations than those required to produce hepatotoxicity. These two organ toxicities were produced only by 3,3',4,4'-TCB despite the fact that equivalent or higher tissue concentrations of 2,2',5,5'-TCB were achieved in vivo in all tissues. We conclude that the in vivo difference in the toxic potency of these two TCB isomers does not result from the significant differences in their tissue disposition, elimination, and ultimate bioaccumulation.

Chiral effects in the induction of drug-metabolizing enzymes using synthetic atropisomers of polychlorinated biphenyls (PCBs)

Atropisomers of the polychlorinated biphenyls 2,2',3,4,4',6-hexachlorobiphenyl (II) and 2,2',3,3',4,4',6,6'-octachlorobiphenyl (III), stable to racemization under physiological conditions, were administered to immature male Sprague-Dawley rats. The racemic hexachlorobiphenyl (II) was found to be a potent (phenobarbital-type) inducer, whereas (+)-II and (-)-II, administered at 100 mumol/kg, showed clearly differing potencies as inducers with (+)-II enhancing aminopyrine N-demethylase, aldrin epoxidase and cytochrome P-450 content more potently than (-)-II. In contrast, the racemic octachlorobiphenyl (III) and its individual enantiomers were only weak phenobarbital-type inducers of cytochrome P-450, and the enantiomers of III were equally (weakly) potent. Separate studies conducted to investigate pharmacokinetic influences on the differential potency of the enantiomers of II showed that after 5 days the concentration of (+)-II in the liver was twice as high as that of its antipode. Therefore, enantioselectivity in disposition as well as in recognition may be responsible for the differential potency seen.

Persistency of highly toxic coplanar PCBs in aquatic ecosystems: uptake and release kinetics of coplanar PCBs in green-lipped mussels (Perna viridis Linnaeus)

The bioaccumulation potential of three highly toxic coplanar PCB isomers [3,3',4,4'-tetrachlorobiphenyl (T(4)CB); 3,3',4,4',5-pentachlorobiphenyl (P(5)CB); and 3,3',4,4',5,5'-hexachlorobiphenyl (H(6)CB)] was investigated using green-lipped mussels (Perna viridis Linnaeus) as a bioindicator, through a transplantation experiment at two locations in Hong Kong waters. By contrast to the relatively rapid uptake and release of many other PCB isomers, the non-ortho chlorine substituted coplanar PCB congeners exhibited slow uptake and clearance. The kinetic parameters of coplanar PCBs based on lipid weight-related data, and the degree of bioaccumulation based on the proportion of coplanar PCBs in total PCBs in mussels, clearly indicate that coplanar PCBs are highly bioaccumulative in lower organisms. On the assumption that mussels are unlikely to be particularly unusual with respect to their bioaccumulation of coplanar PCBs, it appears most likely that these highly toxic and persistent PCB congeners are concentrated by all aquatic organisms, and may reach higher consumers (including humans) in quantities of toxicological concern.

Induction of rat liver microsomal cytochrome P-450 isozymes and epoxide hydrolase by a series of 4'-substituted-2,3,4,5-tetrachlorobiphenyls

We have shown previously that 2,3,4,5-tetrachlorobiphenyl is ineffective as an inducer of rat liver microsomal cytochrome P-450. Addition of a single para-chloro substituent in the otherwise unsubstituted phenyl ring, to give 2,3,4,4',5-pentachlorobiphenyl, produces a potent cytochrome P-450 inducer with both phenobarbital- and 3-methylcholanthrene-type characteristics. In the present study, 2,3,4,5-tetrachlorobiphenyl was substituted in the para(4') position with 12 other functional groups. The 4'-X-C12H5Cl4 derivatives were tested as inducers of cytochromes P-450a--P-450e and epoxide hydrolase, by immunochemical analysis of liver microsomes prepared 4 days after a single treatment (500 mumol/kg) of 1-month-old male Long Evans rats. When the para' substituent was a halogen (F, Cl, Br or I), the derivative induced both cytochromes P-450b and P-450e, and cytochromes P-450c and P-450d, which are the major phenobarbital- and 3-methylcholanthrene-inducible isozymes, respectively. A similar type of induction was observed with a second group of derivatives substituted with CN, NO2 or CF3. However, a derivative containing CH3CO--(which is also a meta-directing, ring-activating substituent) failed to induce cytochromes P-450a-P-450e at the dosage and time tested. Members of a third group of derivatives, which contained an ortho/para-directing, ring-activating substituent) were either ineffective inducers (OH, CH3, CH3O--), or were inducers of cytochromes P-450c and P-450d (isopropyl or t-butyl). Hence, 4'-substitution with a bulky lipophilic substituent conferred 3-methylcholanthrene- but not phenobarbital-type characteristics on 2,3,4,5-tetrachlorobiphenyl. Some of the derivatives tested, namely those substituted with Cl, Br, I and CF3, were remarkably effective inducers of cytochrome P-450a, causing a 10-11-fold induction of this isozyme. Data on the induction of cytochrome P-450c were analyzed by multiparameter linear regression in an attempt to correlate the biological activity of the 4'-X-C12H5Cl4 derivatives with the physiochemical properties of the various substituents. From these results, and those reported recently, we propose that binding of the 4'-X-C12H5Cl4 derivatives to the rat cytosolic Ah receptor is favored by increasing the electronegativity, lipophilicity and hydrogen bonding characteristics of the 4' substituent, whereas enzyme induction (both in vivo and in cultured rat hepatoma cells) is also governed by a fourth characteristic, the STERIMOL factor, which gives a measure of the width of the substituent.(ABSTRACT TRUNCATED AT 400 WORDS)

Increased oxidation of uroporphyrinogen by an inducible liver microsomal system. Possible relevance to drug-induced uroporphyria

1. The hypothesis that uroporphyria-inducing drugs stimulate the oxidation of uroporphyrinogen by a microsomal NADPH-dependent mechanism was tested. 2. 3,4,3',4'-Tetrachlorobiphenyl, a very effective inducer of uroporphyria in chick-embryo hepatocyte cultures, stimulates the NADPH-dependent oxidation of uroporphyrinogen by chick-embryo microsomal fraction in vitro. 3. Two different actions of 3,4,3',4'-tetrachlorobiphenyl are apparently required for this effect: (a) induction of a microsomal system by treatment in vivo and (b) interaction with the induced microsomal fraction in vitro, producing an oxidizing species. 4. The analogue 2,4,2',4'-tetrachlorobiphenyl is relatively ineffective in both the production of porphyria in culture and the stimulation of porphyrinogen oxidation in vitro. 5. Rat hepatocytes do not develop uroporphyria when treated with polychlorinated biphenyls in culture, yet they respond to these drugs with typical induction of cytochrome P-448-dependent drug metabolism. 6. These data provide support for the hypothesis of an increased oxidation of uroporphyrinogen in drug-induced uroporphyria, but also suggest that induction of cytochrome P-448 is not the only factor involved. 7. Both I and III isomers of uroporphyrin and heptacarboxylate porphyrin accumulate when chicken hepatocytes are made uroporphyric by drugs; treatment with desferrioxamine causes a marked decrease in both isomers, suggesting that iron may be involved in the accumulation of both.

PCB problems in the future: foresight from current knowledge

The present paper overviews the forthcoming PCB problems from current knowledge of their use, environmental contamination and toxicology. From a global point of view, PCB levels in the environmental media and biota are unlikely to decline in the near future due to the greater quantities of PCBs still in use than the quantity that has already escaped into the open environment. Considering all the information on the occurrence, distribution and behaviour of PCBs in the ecosystems, the marine mammals are probably the most vulnerable and possible target organisms in forthcoming long-term PCB toxicity. The recent isomer-specific analyses suggest that the intrinsic toxicity of PCBs principally resulted from the coplanar PCB congeners which may impose a greater toxic threat than chlorinated dioxins and furans to humans and wildlife. The measures necessary to reduce further discharge of PCBs into the environment should be set in motion immediately, otherwise there may be a subsequent deleterious biological impact.

Metabolism in vivo of 3,4,3',4'-tetrachlorobiphenyl and toxicological assessment of the metabolites in rats

1. Metabolism in vivo of 3,4,3',4'-tetrachlorobiphenyl (TCB) and toxicological assessment of the metabolites were investigated in the rat. 2. Four metabolites were isolated from faeces of rats dosed with 3,4,3',4'-TCB. Two were identified as 5-hydroxy-3,4,3',4'-TCB and a chlorine-shift metabolite, 4-hydroxy-3,5,3',4'-TCB, by comparison of melting points, chromatographic mobilities and spectral features with those of the synthetic samples. A dihydroxy-TCB and monohydroxy-trichlorobiphenyl were also indicated by mass spectrometry to be excreted in faeces as minor metabolites. 3. Faecal excretion of unchanged 3,4,3',4'-TCB, 5-hydroxy-3,4,3',4'-TCB and 4-hydroxy-3,5,3',4'-TCB was 0.8%, 19.6% and 11.6% of dose, respectively, in 5 days after i.p. injection of 3,4,3',4'-TCB at a dose of 50 mg/kg. 4. From the inability to cause the liver hypertrophy and thymus atrophy, both monohydroxy-metabolites of 3,4,3',4'-TCB are much less toxic than the parent 3,4,3',4'-TCB. In addition, these phenolic metabolites did not induce the activities of benzo[a]pyrene hydroxylase and DT-diaphorase, whereas 3,4,3',4'-TCB greatly induced these activities. These results indicated that unlike PCB congeners with phenobarbital-type inducing ability, 3,4,3',4'-TCB, a prototype of 3-methylcholanthrene-type inducers, is detoxified by metabolic hydroxylation.

Lack of correlation between formation of reactive metabolites and thymic atrophy caused by 3, 4, 3', 4'-tetrachlorobiphenyl in C57BL/6N mice

The possible role of active metabolites of 3, 4, 3', 4'-tetrachlorobiphenyl (TCB) in causing thymic atrophy was investigated using inbred strains of mice. The generation of reactive species which bind covalently to cellular proteins was used to monitor the formation of active TCB metabolites. The amount of in vitro covalent binding of TCB to proteins by liver microsomes was increased markedly by pretreatment of AHH-responsive C57BL/6N mice with either 3-methylcholanthrene (MC) or TCB itself, although these two inducers were not effective in AHH-nonresponsive DBA/2N mice. MC treatment also caused an induction of microsomal TCB-binding activity in all of the (C57BL/6N X DBA/2N) F1 mice. Moreover, among 38 individuals of [(C57BL/6N) (DBA/2N) F1 X DBA/2N] backcross, 23 mice responded to MC with respect to microsomal TCB-binding activity while others did not. These results suggest that the conversion of TCB to protein-bound metabolites is mediated by particular form(s) of cytochrome P-450 which is (are) induced by an Ah receptor mechanism. In order to ascertain whether the active TCB metabolites play a role in causing thymic atrophy, 14C-labeled TCB was administered IP to C57BL/6N mice and the amount of covalent binding of radioactive metabolites to tissue proteins was determined. The in vivo binding was evident in the liver, particularly in the microsomal fraction, on the basis of protein content. In contrast, the thymic proteins contained no measurable amounts of bound radioactivity even when the mice showed marked thymic atrophy. These data suggest that thymic atrophy caused by TCB is not likely to result from the generation of reactive metabolites.

Highly toxic coplanar PCBs: occurrence, source, persistency and toxic implications to wildlife and humans

Isomer-specific determinations of PCB congeners in a wide variety of animal species such as fish, marine mammals (whale, dolphin and porpoise) and terrestrial mammals (dog, cat and human) revealed the environmental occurrence of highly toxic coplanar 3,3',4,4'-tetrachlorobiphenyl (T(4)CB), 3,3',4,4',5-pentachlorobiphenyl (P(5)CB) and 3,3',4,4',5,5'-hexachlorobiphenyl (H(6)CB) within a range of few pg g(-1) to several ten ng g(-1) in fat tissues (except fish) on a wet weight basis. Detection of these toxic residues in wild specimens collected from remote areas such as the North Pacific suggests the already widespread distribution of coplanar PCBs as in the case of general PCB pollution. The clear positive correlations between concentrations of total PCBs and each of the three coplanar PCBs obtained in all mammals analysed suggest that the sources of coplanar PCB contamination to the environment are mainly commercial PCB preparations. Comparison of the composition of three toxic coplanar PCBs in commercial PCB mixtures and in the various animals indicates the relative metabolisability of these congeners as follows: 3,3',4,4'-T4CB>3,3',4,4',5-P5CB>3,3',4,4',5,5'-H6CB. Moreover, marine mammals seem to have lower potency to metabolise the coplanar PCBs in comparison with terrestrial mammals. In human adipose tissues, the concentrations of coplanar PCBs were found to be much higher than 2,3,7,8-tetrachlorodibenzo-p-dioxin (T(4)CDD), 2,3,4,7,8-pentachlorodibenzofuran (P(5)CDF) and other toxic congeners. 'T(4)CDD-equivalent' analysis based on the enzyme induction potencies and the residues of these toxic chemicals indicates that 3,3',4,4',5-P(5)CB may impose a greater toxic threat than dioxins and furans to the humans and probably to wildlife also.

Effect of PCB on some MFO enzyme activities in pregnant and virgin rabbits

Fenclor 64 (a PCB's commercial mixture) was administered twice i.p. to virgin and pregnant New Zealand rabbits at the dose of 100 mg/Kg to evaluate its inducing properties on the following hepatic microsomal MFO activities: p-nitro-anisole-O-demethylase, amino-pyrine-N-demethylase, acetanilide-hydroxylase and aryl-hydrocarbons-hydroxylase. The results indicate that Fenclor 64 evoked a "mixed type" induction in virgin as well as in pregnant rabbits since it increased liver weight, cytochrome P-450 levels, as well as p-nitro-anisole-O-demethylase and acetanilide-hydroxylase. Pregnancy by itself affects only amino-pyrine-N-demethylase levels.

Temporal effects on antipyrine metabolite kinetics in Aroclor 1254-treated rats

The in vivo consequences of a single dose of Aroclor 1254 (50 mg/kg) on the drug metabolizing capacity of rats were investigated. A noninvasive method, employing [N-methyl-14C]-antipyrine where both 14CO2 exhalation and urinary excretion of 4-hydroxy-, 3-hydroxymethyl-, and norantipyrine were monitored, was used. A group of rats were sequentially tested over a 3-week period to characterize temporal patterns. The antipyrine metabolite kinetic approach demonstrated that induction of hepatic cytochrome P-450 is maximal 3-6 days after Aroclor 1254 administration and the effects were apparent for at least a further 14-17 days. Evidence is presented to suggest selective effects of Aroclor 1254 on different cytochromes P-450 are apparent in vivo.

Studies of the influence of chloro-substituent sites and conformational energy in polychlorinated biphenyls on uroporphyrin formation in chick-embryo liver cell cultures

Treatment of cultured chick-embryo liver cells with polychlorinated biphenyls (PCB) results in decreased uroporphyrinogen decarboxylase activity and increased uroporphyrin accumulation. In the present study we examined the effect of the chloro- or bromo-substituent sites in biphenyls (BP) on uroporphyrin accumulation in cultured hepatocytes and the three-dimensional structure of these congeners determined by molecular orbital calculations using a MNDO ('modified neglect of diatomic overlap') method. Among 20 congeners examined, those which were effective in stimulating porphyrin accumulation contained at least two Cl or Br atoms at the lateral adjacent positions in each phenyl ring, e.g. 3,4,3',4'-tetrachloro-, 2,4,3',4'-tetrachloro-, 3,4,5,3',4',5'-hexachloro- and 3,4,5,3',4',5'-hexabromobiphenyl, whereas those which contained less than two halogen atoms or more than three halogen atoms in each phenyl ring or those which contained halogen atoms at 2,2'-positions were not effective. On the basis of the conformational energy (delta E, difference from the most stable conformational energy), which is calculated as a function of the dihedral angle (theta) between the two phenyl rings, biphenyl congeners can be classified into four groups with different conformations. The conformation of active PCB was relatively flexible, whereas inactive species had a rigidly angulated conformation. Furthermore, the calculated probability of the conformation distribution for each congener indicated that the probability of co-planarity was higher for active biphenyls than for inactive congeners. These structural characteristics suggest the significance of both the chloro-substituent sites and the conformational energy reflecting the phenyl-ring twist angles in determining the inhibitory effect of PCB on uroporphyrinogen decarboxylase activity.

Metabolism-related spectral characterization and subcellular distribution of polychlorinated biphenyl congeners in isolated rat hepatocytes

The disposition and biotransformation of 4,4'-dichlorobiphenyl (4-DCB), 2,2',3,3',6,6'-hexachlorobiphenyl (236-HCB), and 2,2',4,4',5,5'-hexachlorobiphenyl (245-HCB) were studied in isolated rat hepatocyte suspensions. The polychlorinated biphenyls (PCBs) were taken up rapidly by the cells but incompletely metabolized. Metabolism followed first-order Michaelis-Menten kinetics for 20 min and plateaued by 60 min, at which point only 32% of 4-DCB (0.005 to 100 microM) and 60% of 236-HCB (0.001 to 100 microM) were metabolized, while metabolism of 245-HCB was not detected (0.1 to 200 microM). Kinetic studies revealed that both 4-DCB and 236-HCB were metabolized by two Michaelis-Menten processes, displaying high- and low-affinity binding. Readdition of congener once metabolism plateaued resulted in a reinitiation of metabolism with the same proportion of metabolites produced. The termination of metabolism was not due to destruction of the mixed-function oxidases or to depletion of cofactors. The metabolism of PCB congeners is influenced by the affinity of the congener for cytochrome P-450 and partitioning of the congener within the hepatocyte. Analysis of absorbance differences (delta absorbance 390-240 nm) of equimolar concentrations of congener (100 microM) revealed that 236-HCB displayed the greatest affinity of binding to cytochrome P-450 followed by 4-DCB, while 245-HCB showed virtually no binding. Microsomal preparations demonstrated equivalent but greater absorbance values. Subcellular distribution of 14C-labeled congener and its metabolites showed that the majority of radioactivity appeared in the cytosolic fraction, representing 70% of the dose added for each congener. Cytosolic binding of congener and metabolites may influence both the availability of congener to cytochrome P-450 and the excretion rate of metabolites from the cell.