Antagonism of aryl hydrocarbon receptor-dependent induction of CYP1A1 and inhibition of IgM expression by di-ortho-substituted polychlorinated biphenyls

Halogenated aromatic hydrocarbons (HAHs) are ubiquitous environment contaminants that produce many of their toxic effects by binding to the aryl hydrocarbon receptor (AhR). However, several investigations have demonstrated that certain polychlorinated biphenyl (PCB) congeners, principally di-ortho-chlorinated PCB congeners, or mixtures containing multiple di-ortho-chlorinated PCBs, inhibit AhR-mediated responses induced by other toxic HAHs. Most relevant to the present study are past reports demonstrating antagonism by these uniquely acting PCB congeners on AhR agonist-mediated inhibition of humoral immune responses. The mechanism responsible for antagonism of AhR agonists by certain PCBs is presently unknown. The present study evaluated the antagonist activity of several di-ortho-substituted PCB congeners [PCB47 (2,2',4,4'), PCB52 (2,2',5,5'), PCB128 (2,2',3,3',4,4'), and PCB153 (2,2',4,4',5,5')] when present in combination with AhR agonists [TCDD (2,3,7,8,-tetrachlorodibenzo-p-dioxin), PCB126 (3,3',4,4',5), and PCB77 (3,3',4,4')] on CYP1A1 induction and inhibition of lipopolysaccharide (LPS)-induced immunoglobulin production in the CH12.LX B cell line. In contrast to non-ortho-substituted PCB (PCB77), which showed additive effects on CYP1A1 induction in combination with TCDD, all of the di-ortho-substituted PCBs examined produced antagonism. Di-ortho-substituted PCB (PCB52) also antagonized TCDD- or PCB126- mediated inhibition of IgM secretion and immunoglobulin heavy chain mRNA expression in the LPS-activated B cells. In addition, PCB52 inhibited TCDD-induced AhR DNA binding to a dioxin-responsive element. Collectively, these results suggest that the mechanism responsible for antagonism by di-ortho-substituted PCB congeners of AhR agonist-mediated CYP1A1 induction and inhibition of antibody responses in B cells occurs through interference with agonist activation of the cytosolic AhR complex.     

Differential relative effect potencies of some dioxin-like compounds in human peripheral blood lymphocytes and murine splenic cells

Human risk assessment for dioxin-like compounds is typically based on the concentration measured in blood serum multiplied by their assigned toxic equivalency factor (TEF). Consequently, the actual value of the TEF is very important for accurate human risk assessment. In this study we investigated the effect potencies of three polychlorinated dibenzo-p-dioxins (PCDDs), six polychlorinated dibenzofurans (PCDFs) and 10 polychlorinated biphenyls (PCBs) relative to the reference congener 2,3,7,8-tetrachloro-dibenzo-p-dioxin (TCDD) in in vitro exposed primary human peripheral blood lymphocytes (PBLs) and mouse splenic cells. REPs were determined based on cytochrome P450 (CYP) 1A1, 1B1 and aryl hydrocarbon receptor repressor (AhRR) gene expression as well as CYP1A1 activity in human PBLs and Cyp1a1 gene expression in murine splenic cells. Estimated median human REPs for 1,2,3,4,6,7,8-heptachlorodibenzo-p-dioxin (1234678-HpCDD), 2,3,4,7,8,-pentachlorodibenzofuran (23478-PeCDF), 1,2,3,4,7,8-hexachlorodibenzofuran (123478-HxCDF) and 1,2,3,4,7,8,9-heptachlorodibenzofuran (1234789-HpCDF) were with 0.1, 1.1, 1 and 0.09, respectively, significantly higher compared to those estimated for mouse with REPs of 0.05, 0.45, 0.09 and 0.04, respectively. Opposite to these results, the estimated median human REP of 3,3′,4,4′,5-pentachlorobiphenyl (PCB 126), was with 0.001 30-fold lower compared to the mouse REP of 0.03. Furthermore, human REPs for 1234678-HpCDD, 23478-PeCDF, 123478-HxCDF, 1234789-HpCDF and PCB 126 were all outside the ± half log uncertainty range that is taken into account in the WHO-assigned TEFs. Together, these data show congener- and species-specific differences in REPs for some, but not all dioxin-like congeners tested. This suggests that, more emphasis should be placed on human-tissue derived REPs in the establishment of a TEF for human risk assessment.     

The anti-estrogenicity of Ah receptor agonists in carp (Cyprinus carpio) hepatocytes.

Cultured hepatocytes of female carp (Cyprinus carpio) were coexposed for 4 days to 200 nM 17beta-estradiol (E2), and concentration ranges of nine known Ah receptor (AhR) agonists: 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 3,3'4,4'5-pentachlorobiphenyl (PCB 126), 2,3'4,4'5-pentachlorobiphenyl (PCB 118), beta-naphthoflavone (BNF), benzo(a)pyrene (BaP), benzo(a)anthracene (BaA), diindolylmethane (DIM), 6-methyl-1,3,8-trichlorodibenzofuran (MCDF) and hexachlorobenzene (HCB). TCDD caused a greater than 100-fold induction of cytochrome P4501A (CYP1A) activity, measured as ethoxyresorufin O-deethylase (EROD), with an EC50 of 6 pM. Based on EC50 values, the order of potency as CYP1A inducers was TCDD > PCB 126 > BNF > BaP > BaA > PCB 118. DIM and MCDF caused a lower maximum CYP1A induction (< 9-fold), whereas HCB caused no EROD induction at concentrations up to 6 microM. TCDD, PCB 126, BNF, BaP, and DIM also caused a concentration-dependent suppression of the secretion of the yolk protein vitellogenin (Vtg), relative to E2-treated hepatocytes. Suppression of Vtg secretion was not directly correlated with EROD activity, and the antiestrogenic effects occurred at higher concentrations than the induction of CYP1A. This indicates that the anti-estrogenicity was not caused by increased metabolism of E2 due to induction of CYP1A. Nevertheless, the order of potency of the tested compounds for suppression of Vtg secretion was comparable to the order of potency for CYP1A induction. This concurrence suggests that the anti-estrogenicity of these compounds is AhR-mediated, but does not involve CYP1A. This could be relevant for feral fish populations, as they are frequently exposed to AhR agonists, to an extent that AhR-mediated effects are observed.     

Inducing effects of dioxin-like polychlorinated biphenyls on CYP1A in the human hepatoblastoma cell line HepG2, the rat hepatoma cell line H4IIE, and rat primary hepatocytes: comparison of relative potencies.

Polychlorinated biphenyls (PCBs) are a group of widespread environmental pollutants. Some non-ortho-substituted congeners with a high likelihood of coplanarity of both aromatic rings have been shown to act like 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) as agonists of the aryl hydrocarbon receptor (AhR) subsequently leading to adverse effects, such as immunosuppression and tumor promotion. Although there is a broad base of experimental data concerning the toxicity of PCBs in laboratory animals and animal-derived primary cells and cell lines, only few experimental data are available for cells of human origin. As a parameter of AhR activation, induction of CYP1A-mediated 7-ethoxyresorufin O-deethylase (EROD) activity was determined in the human hepatoblastoma cell line HepG2 treated with the PCBs IUPAC Nos. 77, 81, 105, 114, 118, 123, 126, 156, 157, 167, 169, and 189, and with TCDD as a positive control. Compared with results in rat primary hepatocytes and the rat hepatoma cell line H4IIE, treated HepG2 cells showed lower specific EROD activities maximally inducible by TCDD and PCBs, and EC50 values were shifted to higher concentrations. Furthermore, relative potency factors (REPs) for some congeners such as PCBs 81, 126, and 169 greatly differed from those observed in cells derived from rats. Northern blot analyses showed that EROD activities run parallel to changes in CYP1A-specific mRNA contents. The considerable differences in EROD-derived REPs between cells of human and rat origin indicate the need for further investigations in experimental models from different species including humans in order to extend the database of biochemical and toxic responses to PCBs.     

Relative contributions of affinity and intrinsic efficacy to aryl hydrocarbon receptor ligand potency

Models of receptor action are valuable for describing properties of ligand-receptor interactions and thereby contribute to mechanism-based risk assessment of receptor-mediated toxic effects. In order to build such a model for the aryl hydrocarbon receptor (AHR), binding affinities and CYP1A induction potencies were measured in PLHC-1 cells and were used to determine intrinsic efficacies for 10 halogenated aromatic hydrocarbons (HAH): 2,3,7, 8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,7, 8-tetrachlorodibenzofuran (TCDF), and eight polychlorinated biphenyls (PCB). TCDD, TCDF, and non-ortho-substituted PCBs 77, 81, 126, and 169 behaved as full agonists and displayed high-intrinsic efficacy. In contrast, the mono- and di-ortho-substituted PCBs bound to the AHR but displayed lower or no intrinsic efficacy. PCB 156 was a full agonist, but with an intrinsic efficacy 10- to 50-fold lower than non-ortho-substituted PCBs. PCB 118 was a very weak partial agonist. PCBs 105 and 128 were shown to be competitive antagonists in this system. The model was then used to predict CYP1A induction by binary mixtures. These predictions were tested with binary mixtures of PCB 126, 128, or 156 with TCDD. Both PCB 156 (a low-intrinsic efficacy agonist) and PCB 128 (a competitive antagonist) inhibited the response to TCDD, while the response to TCDD and PCB126 was additive. These data support the following conclusions: 1) only 1-2% of the receptors in the cell need be occupied to achieve 50% of maximal CYP1A induction by one of the high-intrinsic efficacy agonists, demonstrating the existence of "spare" receptors in this system; 2) the insensitivity of fish to ortho-substituted PCBs is due to both reduced affinity and reduced intrinsic efficacy compared to non-ortho-substituted PCBs; 3) PCB congeners exhibit distinct structure-affinity and structure-efficacy relationships. Separation of AHR ligand action into the properties of affinity and intrinsic efficacy allows for improved prediction of the behavior of complex mixtures of ligands, as well as mechanistic comparisons across species and toxic endpoints.     

TCDD and PCBs inhibit breast cancer cell proliferation in vitro

The effects on cell proliferation of arylhydrocarbon receptor (AhR) agonists in estrogen-responsive T47D and ZR-75-1 cells were investigated. 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) and the non-ortho-substituted polychlorinated biphenyl (PCB) congeners, PCB 77, PCB 81, PCB 126, and PCB 169 each inhibited 17β-estradiol (E₂)-stimulated cell proliferation in a dose–responsive manner. In the absence of added E₂, TCDD, PCB 77, PCB 81, and PCB 169 had no significant effect on cell proliferation, while PCB 126 at high concentrations caused slight elevations. The order of effective inhibition of E₂-stimulated cell proliferation by the PCB congeners was: PCB 81>PCB 126PCB 169>PCB 77. In the comparative literature, mammalian TEFs for these congeners toxic potency are in the order: PCB 126>PCB 169>PCB 81PCB 77 [Organohalogen Compd. 34 (1997) 237]. Our results thus show an unexpected different pattern for the inhibitory effects of PCBs congeners on E₂-mediated cell proliferation.     

Polychlorinated biphenyl exposure and CYP19 gene regulation in testicular and adrenocortical cell lines.

Exposure to polychlorinated biphenyls (PCBs) disturbs many estrogen-mediated biochemical processes. PCBs may cause these abnormalities by altering expression of the aromatase gene CYP19. This study demonstrated that high concentrations of PCB126 increased basal CYP19 mRNA abundance in mouse testicular Leydig I-10 cells and human adrenocortical H295R cells. Stimulating the cells with chorionic gonadotropin or 8-Br-cAMP concealed the estrogenic effect of PCB126. PCB126 is a powerful ligand for nuclear receptor AhR. Antagonizing the AhR activity of H295R by an inhibitor abolished PCB126-elicited CYP19 induction. However, PCB126 elevated basal CYP19 expression and aromatase activity in a slow progressive manner contrary to the sharp induction of the classic AhR target gene CYP1A1. Exposure of H295R to PCBs with different AhR activation abilities also varied CYP19 and CYP1A1 expression in dissimilar patterns, although the CYP19 mRNA levels were in line with the AhR activation abilities of the congeners. In contrast to PCB126, PCB39, which could not activate AhR and lacked effect on CYP1A1, significantly reduced CYP19 mRNA expression. AhR apparently played an important role in CYP19 gene regulation, but it might regulate CYP19 differently from CYP1A1 in the adrenocortical cells. Regardless of the action mechanism, PCB exposure increases risk for CYP19 dysregulation.     

A comparative study on the effects of 2,3,7,8,-tetrachlorodibenzo-p-dioxin polychlorinated biphenyl126 and estrogen in human bronchial epithelial cells

Epidemiological studies on 2,3,7,8,-tetrachlorodibenzo-p-dioxin (TCDD) exposure indicated high incidences of pulmonary dysfunctions and lung cancer. Animal studies also demonstrated lung cancer development in female, but not in male, rats exposed to TCDD. Such effects, however, have not been reported in polychlorinated biphenyls (PCB) exposure. In our present study, we have investigated the effects of TCDD and PCB126, with or without cotreatment with 17 beta-estradiol (E2), on a human bronchial epithelial cell line BEAS-2B. We found that treatment with either TCDD or PCB126 alone reduced cell numbers as well as thymidine incorporation. Cell death, however, was only detected in PCB126-, but not TCDD-, treated cultures. The TCDD-induced cell reduction, therefore, could not be contributed to cell death. Meanwhile, because TCDD- and PCB126-enhanced CYP1A1 and CYP1B1 expressions were significantly reduced by the AhR antagonist and CYP1 inhibitor alpha-naphthoflavone (ANF), this indicated that the effects of TCDD and PCB126 were AhR and cytochrome p450 1 dependent. We also found that while E2 itself did not alter CYP1A1 and CYP1B1 expressions, cotreatment of E2 with TCDD or PCB126 would significantly enhance TCDD-, but not PCB126-, induced toxicity. We further demonstrated that in the presence of E2, 1 nM TCDD increased the production of E2 metabolites, 2-methoxyestradiol (2-MeOE2) and 4-methoxyestradiol (4-MeOE2). PCB126, however, only increased 2-MeOE2 formation without significant induction of 4-MeOE2. We believe that these metabolites, especially 4-MeOE2, interacted with TCDD to further suppress cell growth. Our data provided the first demonstration on the enhancement of TCDD-induced toxicity in human lung cells via interaction with estrogen.     

Relative potency based on hepatic enzyme induction predicts immunosuppressive effects of a mixture of PCDDS/PCDFS and PCBS

The toxic equivalency factor (TEF) approach was employed to compare immunotoxic potency of mixtures containing polychlorinated dibenzo-p-dioxins, polychlorinated dibenzofurans and polychlorinated biphenyls relative to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), using the antibody response to sheep erythrocytes (SRBC). Mixture-1 (MIX-1) contained TCDD, 1,2,3,7,8-pentachlorodibenzo-p-dioxin (PeCDD), 2,3,7,8-tetrachlorodibenzofuran (TCDF), 1,2,3,7,8-pentachlorodibenzofuran (1-PeCDF), 2,3,4,7,8-pentachlorodibenzofuran (4-PeCDF), and 1,2,3,4,6,7,8,9-octachlorodibenzofuran (OCDF). Mixture-2 (MIX-2) contained MIX-1 and the following PCBs, 3,3',4,4'-tetrachlorobiphenyl (IUPAC No. 77), 3,3',4,4',5-pentachlorobiphenyl (126), 3,3',4,4',5,5N-hexachlorobiphenyl (169), 2,3,3',4,4'-pentachlorobiphenyl (105), 2,3',4,4',5-pentachlorobiphenyl (118), and 2,3,3',4,4',5-hexachlorobiphenyl (156). The mixture compositions were based on relative chemical concentrations in food and human tissues. TCDD equivalents (TEQ) of the mixture were estimated using relative potency factors from hepatic enzyme induction in mice [DeVito, M.J., Diliberto, J.J., Ross, D.G., Menache, M.G., Birnbaum, L.S., 1997. Dose-response relationships for polyhalogenated dioxins and dibenzofurans following subchronic treatment in mice. I .CYP1A1 and CYP1A2 enzyme activity in liver, lung and skin. Toxicol. Appl. Pharmacol. 130, 197-208; DeVito, M.J., Menache, G., Diliberto, J.J., Ross, D.G., Birnbaum L.S., 2000. Dose-response relationships for induction of CYP1A1 and CYP1A2 enzyme activity in liver, lung, and skin in female mice following subchronic exposure to polychlorinated biphenyls. Toxicol. Appl. Pharmacol. 167, 157-172] Female mice received 0, 1.5, 15, 150 or 450 ng TCDD/kg/day or approximately 0, 1.5, 15, 150 or 450 ng TEQ/kg/day of MIX-1 or MIX-2 by gavage 5 days per week for 13 weeks. Mice were immunized 3 days after the last exposure and 4 days later, body, spleen, thymus, and liver weights were measured, and antibody response to SRBCs was observed. Exposure to TCDD, MIX-1, and MIX-2 suppressed the antibody response in a dose-dependent manner. Two-way ANOVA indicated no differences in the response between TCDD and the mixtures for body weight, spleen/body weight and decreased antibody responses. The results support the use of the TEF methodology and suggest that immune suppression by dioxin-like chemicals may be of concern at or near background human exposures.     

Species difference in the regulation of cytochrome P450 2S1: lack of induction in rats by the aryl hydrocarbon receptor agonist PCB126

CYP2S1 is an evolutionarily conserved, mainly extra-hepatic member of the CYP2 family and proposed to be regulated by the aryl hydrocarbon receptor (AhR). The present study explores AhR's regulation of CYP2S1 in male Sprague Dawley rats using PCB126 (3,3',4,4',5-pentachlorobiphenyl), the most potent AhR agonist among the PCBs. Additionally, CYP2S1 expression was examined after treatments with the classic CYP-inducers β-naphthoflavone (β-NF, AhR activator), phenobarbital (PB, CAR activator) and dexamethasone (Dex, PXR activator). CYP2S1 and CYP1A1/2, CYP1B1, CYP2B and CYP3A mRNAs were measured in liver, lung, spleen, stomach, kidney, and thymus at different time points. Constitutive CYP2S1 was expressed at comparable levels to other CYPs with the highest expression levels in stomach, kidney and lung. CYP2S1 mRNA was only non-significantly elevated by β-NF in liver tissues. PCB126 did not increase CYP2S1 mRNA in any organ and at any time point examined despite a significant induction of CYP1 genes. PCB126 reduced CYP2S1 mRNA by 40% (not significant) from the 7th post-exposure day in thymus. PB and Dex had no effect on CYP2S1 mRNA levels. These observations show that in this model CYP2S1 is not, or only weakly, regulated by AhR and not induced by CAR or PXR activators.     

CYP1A1-inducing potency in H4IIE cells and chemical composition of technical mixtures of polychlorinated biphenyls

Polychlorinated biphenyls (PCBs) are present in environmental and tissue samples as complex mixtures of dioxin-like and non-dioxin-like congeners. Induction of cytochrome (CYP) P4501A1-catalyzed 7-ethoxyresorufin-O-deethylase (EROD) activity in H4IIE hepatoma cells is widely used as a simple in vitro bioassay for the dioxin receptor-mediated biological action of dioxin-like agonists. Since the results of the assay may be influenced indirectly by abundant non-dioxin-like PCBs, its application to the bioanalysis of complex PCB mixtures was studied. In the PCB mixtures Arochlor 1254 and Clophen A50, potent dioxin-like non-ortho PCBs and polychlorinated dibenzofurans (PCDFs) were found in minor amounts. However, the non-ortho PCBs accounted for most of the overall 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) equivalents based on EROD induction (EROD-TEQs). A comparison with a pattern of toxic equivalents (TEQs) based on toxic equivalency factors (I-TEFs) recently suggested in an international report revealed a much higher relative impact of mono-ortho PCBs on I-TEQs than on EROD-TEQs while total EROD-TEQs approximately coincided with total I-TEQs. It is concluded that the H4IIE bioassay is useful to assess total I-TEQs but does not reflect the individual contributions of PCB subgroups because of a higher evaluation of mono-ortho and di-ortho PCBs by I-TEFs. Based on individual EROD-TEFs, slightly higher mean EROD-TEQs than those calculated by assuming additive behaviour of single PCBs were obtained. This finding suggests a minor synergistic influence of non-dioxin-like PCBs on the inducing potency of dioxin-like agonists in the H4IIE bioassay.     

Ethoxyresorufin-O-deethylase (EROD) induction by TCDD,PeCDF and PCB 126 in bobwhite quail hepatocytes

World Health Organization (WHO) toxic equivalency factors are used to calculate toxic equivalent (TEQ) concentrations of complex mixtures of dioxin-like compounds (DLCs), such as polychlorinated dibenzo-p-dioxins, polychlorinated dibenzofurans and polychlorinated biphenyls (PCBs), for mammals, fish and birds. The TEQ concept assumes that all species of a taxa respond with similar sensitivity to individual DLCs, but several reports do not support this assumption for birds. Our laboratory is conducting research to attempt to uncover the fundamental mechanism(s) underlying the reasons why avian species differ in sensitivity to DLCs. The present study determined concentration-dependent effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,4,7,8-pentachlorodibenzofuran (PeCDF) and 3,3′,4,4′,5-pentachlorobiphenyl (PCB 126) on ethoxyresorufin-O-deethylase (EROD) activity in primary cultures of northern bobwhite quail (Colinus virginianus) hepatocytes. Bobwhite quail were studied because (1) this species is used in the laboratory for toxicity testing and (2) the amino acids at all locations within the ligand binding domain (LBD) of aryl hydrocarbon receptor 1 (AHR1) in bobwhite quail and ring necked pheasant (Phasianus colchicus) are identical. Because earlier work indicated the importance of the identity of amino acids at key sites within the AHR1 LBD, we hypothesized that bobwhite quail and ring necked pheasant hepatocytes should have similar sensitivity to EROD induction by DLCs. EC_threshold-based relative sensitivity of the bobwhite quail compared to chicken for TCDD, PeCDF and PCB 126 was 0.11, 0.17 and 0.02, respectively. The rank order of potency was PeCDF > TCDD > PCB 126. The results confirm that bobwhite quail and ring-necked pheasant hepatocytes have similar sensitivity to EROD induction by TCDD, PeCDF and PCB 126.