Methoxychlor suppresses the 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-inducible CYP1A1 expression in murine Hepa-1c1c7 cells

Methoxychlor (MXC) is a pesticide that was developed as a replacement for dichlorodiphenyltrichloroethane (DDT). The influence of MXC on CYP1A1 expression or the functions of mouse hepatoma Hepa-1clc7 remain unclear. Cultured Hepa-1c1c7 cells were treated with MXC with or without 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) to assess the role of MXC on CYP1A1 expression. MXC alone did not affect CYP1A1-specific 7-ethoxyresorufin O-deethylase (EROD) activity. In contrast, TCDD-inducible EROD activities were markedly reduced upon concomitant treatment with TCDD and MXC in a concentration-dependent manner. Treatment with ICI 182.780, an estrogen-receptor antagonist, did not affect the suppressive effects of MXC on TCDD-inducible EROD activity. TCDD-inducible CYP1A1 mRNA levels were markedly suppressed upon treatment with TCDD and MXC, and this is consistent with their effects on EROD activity. A transient transfection assay using dioxin-response element (DRE)-linked luciferase and an electrophoretic mobility shift assay revealed that MXC reduced the transformation of the aryl hydrocarbons (Ah) receptor to a form capable of specifically binding to the DRE sequence in the promoter region of the CYP1A1 gene. These results suggest that the downregulation of CYP1A1 gene expression by MXC in Hepa-1c1c7 cells might be an antagonism of the DRE binding potential of the nuclear Ah receptor but is not mediated through the estradiol receptor.     

Suppression of CYP1A1 expression by naringenin in murine Hepa-1c1c7 cells

Naringenin, dietary flavonoid, is antioxidant constituents of many citrus fruits. In the present study, we investigated the effect of naringenin on 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-inducible CYP1A1 gene expression in mouse hepatoma Hepa-1c1c7 cells. Naringenin alone did not affect CYP1A1-specific 7-ethoxyresorufin O-deethylase (EROD) activity. In contrast, the TCDD-inducible EROD activities were markedly reduced upon concomitant treatment with TCDD and naringenin in a dose dependent manner. TCDD-induced CYP1A1 mRNA level was also markedly suppressed by naringenin. A transient transfection assay using dioxin-response element (DRE)-linked luciferase and electrophoretic mobility shift assay revealed that naringenin reduced transformation of the aryl hydrocarbons receptor(AhR) to a form capable of specifically binding to the DRE sequence in the promoter of the CYP1A1 gene. These results suggest the down regulation of the CYP1A1 gene expression by either naringenin in Hepa-1c1c7 cells might be antagonism of the DRE binding potential of nuclear AhR.     

Cytokine-mediated suppression of cytochrome P450 1A1 in Hepa-1c1c7 cells by pokeweed mitogen

This study investigated the effects of pokeweed mitogen (PWM) on the regulation of cytochrome P450 (P450) 1A1 expression in an in vitro model, using murine hepatoma cell line Hepa-1c1c7 and murine macrophage cell line RAW 264.7 cell cultures. PWM added directly to Hepa-1c1c7 cells had no effect on 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-induced P450 1A1-specific 7-ethoxyresorufin O-deethylase (EROD) activity. However, TCDD-induced EROD activity and P450 1A1 mRNA levels were markedly suppressed when Hepa-1c1c7 cells were cultured with PWM-treated conditioned media from RAW 264.7 in a dose-dependent manner. Concomitant treatment with PWM and pentoxifylline, a TNFalpha synthesis inhibitor, to RAW 264.7 cells decreased the suppressive effects of PWM on TCDD-induced EROD activity. In PWM-exposed RAW 264.7 cell cultures, TNFalpha and IL-6 levels increased in a dose-dependent fashion. When antibodies to TNFalpha or/and IL-6 were added to PWM-treated conditioned media from RAW 264.7, the suppression of EROD activity was inhibited. These results suggested the suppression of P450 1A1 by PWM was mediated exclusively by TNFalpha and IL-6, released from macrophages.     

Polybrominated diphenyl ethers as Ah receptor agonists and antagonists.

Polybrominated diphenyl ethers (PBDEs) have been identified in every compartment of the environment and biota due to their widespread use as flame retardants. There is debate over their potential to threaten environmental and human health due to insufficient toxicological information. The weak to moderate binding affinity of PBDE congeners to the Ah receptor (AhR) and the weak induction of EROD (ethoxyresorufin-O-deethylase) activity suggest the possibility of dioxin-like behavior. We have investigated whether PBDE congeners act as Ah receptor agonists or antagonists at sequential stages of the AhR signal transduction pathway leading to CYP1A1. PBDE congeners 77, 119, and 126 were moderately active towards DRE (dioxin response element) binding and induced responses of both CYP1A1 mRNA and CYP1A1 protein equivalent to the maximal response of TCDD (2,3,7,8-tetrachlorodibenzo-p-dioxin) in primary Sprague-Dawley rat hepatocytes, although at concentrations three to five orders of magnitude greater than TCDD. These congeners showed additive (throughout this article, we use additive and antagonistic as shorthand terms for increasing or decreasing the response observed with TCDD alone) behavior towards DRE binding with 10(-9) M TCDD, whereas most other PBDE congeners antagonized the action of TCDD. PBDEs 100, 153, and 183 were very weak activators of DRE binding; other congeners and the commercial "penta," "octa," and "deca" bromodiphenyl ether mixtures were inactive. The environmentally prominent congeners 47 and 99 were inactive at all stages of signal transduction, and the "penta" mixture had negligible ability to induce EROD activity. We suggest that current concentrations of PBDEs in biota contribute negligibly to dioxin-like toxicity compared with other environmental contaminants, such as polychlorinated dibenzo-p-dioxins and polychlorinated biphenyls.     

Effect of biochanin A on the aryl hydrocarbon receptor and cytochrome P450 1A1 in MCF-7 human breast carcinoma cells

Phytoestrogen biochanin A is an isoflavone derivative isolated from red clover Trifolium pratense with anticarcinogenic properties. This study examined the action of biochanin A with the carcinogen activation pathway that is mediated by the aryl hydrocarbon receptor (AhR) in MCF-7 breast carcinoma cells. Treating the cells with biochanin A alone caused the accumulation of CYP1A1 mRNA and an increase in CYP1A1-specific 7-ethoxyresorufin O-deethylase (EROD) activity in a dose dependent manner. A concomitant treatment with 7,12-dimethylbenz[a]anthracene (DMBA) and biochanin A markedly reduced the DMBA-inducible EROD activity and CYP1A1 mRNA level. In addition, the biochanin A treatment alone activated the DNA-binding capacity of the AhR for the dioxin-response element (DRE) of CYP1A1, as measured by the electrophoretic-mobility shift assay (EMSA). EMSA revealed that biochanin A reduced the level of the DMBA-inducible AhR-DRE binding complex. Furthermore, biochanin A competed with the prototypical AhR ligand, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), for binding to the AhR in an isolated rat cytosol. The biochanin A competitively inhibited the metabolic activation of DMBA, as measured by the formation of the DMBA-DNA adducts. These results suggest that biochanin A may thus be a natural ligand to bind on AhR. Therefore, biochanin A may be due to act an antagonist/agonist of the AhR pathway.     

Estradiol enhances and estriol inhibits the expression of CYP1A1 induced by 2,3,7,8-tetrachlorodibenzo-p-dioxin in a mouse ovarian cancer cell line

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a ubiquitous pollutant and promoter of carcinogenesis. This study investigated the interaction between TCDD and different estrogens in a cancer cell line (ID8) derived from mouse ovarian epithelium. TCDD-induced ethoxyresorufin-O-deethylase (EROD) activity and cytochrome P4501A1 (CYP1A1) expression in a dose- and time-dependent manner. Estrogen receptor (ER) alpha mRNAs were constitutively expressed, but ER beta and progesterone receptor (PR) mRNAs were not expressed. Induction of EROD by TCDD was completely inhibited by a alpha-naphthoflavone and phenanthroline, two aryl hydrocarbon receptor (AhR) antagonists. Progesterone and gonadotropins (FSH and LH) had no effect on the induction of EROD by TCDD. Congeners of 17beta-estradiol (E2) increased the induction of EROD activity by TCDD dose-dependently in the relative potency order: estrone (El)>E2> or = 4-hydroxyestradiol (4OHE2)> or = 2-hydroxyestradiol (2OHE2). In contrast, estriol (E3) decreased EROD activity induced by TCDD. E2 increased TCDD-induced CYP1A1 protein and mRNA whereas E3 decreased both the protein and mRNA. E2 did not alter luciferase activity induced by TCDD in cells transfected with a luciferase reporter containing dioxin response elements (DRE) or a CYP1A1 promoter. In contrast, E3 dose-dependently decreased the luciferase activity. A pure anti-estrogen (ICI 182780) inhibited the interaction between E2 and TCDD but did not block E3's effect on EROD activity. These results indicate that E2 may affect TCDD-induced CYP1A1 expression by a mechanism different from E3 in ID8 cells. It appears that the potentiation of E2 in the induction of CYP1A1 by TCDD occurs by a mechanism involving ER alpha since a specific ER antagonist blocked the potentiation. The inhibitory effect of E3 may be due to a rapid direct effect on EROD and a later suppression of CYP1A1 expression.     

Effect of troglitazone on CYP1A1 induction

Several peroxisome proliferators enhance CYP1A1 activity, but the mechanisms involved in this enhancement remain unknown. In this study, we examined the effect of troglitazone, a peroxisome proliferator-activated receptor-gamma (PPAR-gamma) agonist, on CYP1A1 gene expression and explored the mechanisms involved in these effects. Troglitazone increased gene expression of CYP1A1 mRNA and also increased CYP1A1-specific 7-ethoxyresorufin-O-deethylase (EROD) activity in a dose-dependent manner. Moreover, concomitant treatment with troglitazone and GW9662, a PPAR antagonist, markedly reduced the troglitazone-inducible EROD activity. Luciferase reporter assays using Hepa-1c1c7 cells showed a significant transactivation by troglitazone with a reporter plasmid containing a region from -1395 to +7 of the CYP1A1 gene. We found that a putative peroxisome proliferator-response element (PPRE) between -521 and -500 is located in the CYP1A1 gene promoter. Their inactivation by deletion mutagenesis suppressed the inductive effect of troglitazone on CYP1A1 promoter activation. Electrophoretic mobility shift assay revealed that troglitazone induced the activation of the PPAR-gamma to a form capable of binding specifically to the PPRE sequence of the CYP1A1 gene promoter. Furthermore, troglitazone increased the formation of the benzo[a]pyrene (BaP)-DNA adduct. Overall, our results suggest that troglitazone induces CYP1A1 enzyme activity and gene expression through PPAR-gamma activation, and may be involved in carcinogenesis.     

Induction of cytochrome P450IA1 in mouse hepatoma cells by several chemicals. Phenobarbital and TCDD induce the same form of cytochrome P450

The mouse hepatoma cell line Hepa-1 was studied for aryl hydrocarbon hydroxylase (AHH) inducibility by sixteen compounds known to be inducers of cytochrome P450 of different "classes". Both 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and sodium phenobarbital induced AHH activity. A cytochrome P450IA1-specific (P1-450) mouse cDNA probe was used to quantitate mRNA induction. There was a good correlation between the amount of cytochrome P450IA1 mRNA induced and AHH activity. Immunoblots with monoclonal antibody 1-7-1, which recognizes rat liver P450IA1 and P450IA2 (P450c and P450d, respectively), showed that both phenobarbital and TCDD increase the amount of a P450 isozyme immunorelated to P450IA1 in this cell line. Hepa-1 mutants with no AHH inducibility (no functional P450IA1 structural gene; no Ah receptor; no nuclear translocation of the inducer-receptor complex; and presence of dominant repressor) did not respond to phenobarbital. The cytosolic receptor for TCDD (Ah receptor) was characterized to see if phenobarbital induced cytochrome P450IA1 mRNA and the hydroxylase enzyme through the same mechanism as TCDD. 20 mM Phenobarbital almost completely abolished the binding of 3H-TCDD to the cytosolic receptor. These data indicate that phenobarbital can be a weak ligand for the Ah receptor and thus induce cytochrome P450IA1 and AHH activity. The observation increases the list of different P450 forms inducible by phenobarbital.     

6-Methyl-1,3,8-trichlorodibenzofuran as a 2,3,7,8-tetrachlorodibenzo-p-dioxin antagonist: inhibition of the induction of rat cytochrome P-450 isozymes and related monooxygenase activities

In addition to being one of the most toxic chemicals known, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) is the most potent inducer of rat liver microsomal cytochrome P-4501A1 (P-450c). Previous studies have demonstrated that a high affinity, low capacity cytosolic receptor (the Ah receptor) mediates the activity of TCDD to induce cytochrome P-4501A1, which catalyzes benzo[a]pyrene hydroxylation [aryl hydrocarbon hydroxylase (AHH]) and 7-ethoxyresorufin O-dealkylation (EROD). The results of the present study indicate that 6-methyl-1,3,8-trichlorodibenzofuran (MCDF) effectively competes with [3H]TCDD for binding to the Ah receptor in rat liver cytosol. The concentration of MCDF effecting 50% displacement of [3H]TCDD was 4.9 X 10(-8) M, which is approximately 50 times greater than the EC50 for unlabeled TCDD (approximately 1 X 10(-9) M). However, in contrast to TCDD, MCDF was only a weak inducer of AHH and EROD activity in rat hepatoma H-4-II cells in culture. When co-incubated, MCDF diminished in a concentration-dependent manner the ability of TCDD to induce AHH and EROD activity in vitro. Treatment of rats with 20-200 mumol/kg MCDF in vivo had little or no effect on liver microsomal AHH and EROD activity, whereas treatment of rats with 16 nmol/kg TCDD caused a 6- and a 70-fold induction of AHH and EROD activity, respectively. When co-administered, MCDF diminished by approximately 50% the ability of TCDD to induce AHH and EROD activity in vivo. The partial antagonism produced by 50 mumol/kg MCDF could be partially overcome by doubling the dosage of TCDD from 16 to 32 nmol/kg. Immunochemical analysis of rat liver microsomes revealed that treatment of rats with 20-200 mumol/kg MCDF caused little or no induction of cytochromes P-4501A1 and P-4501A2 (P-450d), whereas these isozymes were induced 33- and 5-fold, respectively, in rats treated with 16 nmol/kg TCDD. When co-administered, MCDF diminished by approximately 50% the ability of TCDD to induce cytochrome P-4501A1 in vivo, which established that MCDF was not simply acting as an inhibitor of AHH and EROD activity. MCDF also antagonized the ability of TCDD to induce cytochrome P-4501A2, which suggests that the induction of both cytochromes P-4501A1 and P-4501A2 is regulated by the Ah receptor. These results indicate that MCDF binds with high affinity to the Ah receptor in rat liver cytosol and competitively blocks the binding of TCDD.(ABSTRACT TRUNCATED AT 400 WORDS)     

Interactions of polybrominated diphenyl ethers with the aryl hydrocarbon receptor pathway.

Polybrominated diphenyl ethers (PBDEs) are brominated flame retardants that have been in use as additives in various consumer products. Structural similarities of PBDEs with other polyhalogenated aromatic hydrocarbons that show affinity for the aryl hydrocarbon receptor (AhR), such as some polychlorinated biphenyls, raised concerns about their possible dioxin-like properties. We studied the ability of environmentally relevant PBDEs (BDE-47, -99, -100, -153, -154, and -183) and the "planar" congener BDE-77 to bind and/or activate the AhR in stably transfected rodent hepatoma cell lines with an AhR-responsive enhanced green fluorescent protein (AhR-EGFP) reporter gene (H1G1.1c3 mouse and H4G1.1c2 rat hepatoma). 7-Ethoxyresorufin-O-deethylation (EROD) was used as a marker for CYP1A1 activity. Dose- and bromination-specific inhibition of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-induced responses was measured by their ability to inhibit the induction of AhR-EGFP expression and EROD activity. Individual exposure to these PBDEs did not result in any increase in induction of AhR-EGFP or CYP1A1 activity. The lower brominated PBDEs showed the strongest inhibitory effect on TCDD-induced activities in both cell lines. While the highest brominated PBDE tested, BDE-183, inhibited EROD activity, it did not affect the induction of AhR-EGFP expression. Similar findings were observed after exposing stably transfected human hepatoma (xenobiotic response element [XRE]-HepG2) cells to these PBDEs, resulting in a small but statically significant agonistic effect on XRE-driven luciferase activity. Co-exposure with TCDD resulted again in antagonistic effects, confirming that the inhibitory effect of these PBDEs on TCDD-induced responses was not only due to direct interaction at receptor level but also at DNA-binding level. This antagonism was confirmed for BDE-99 in HepG2 cells transiently transfected with a Gal4-AhR construct and the corresponding Gal4-Luc reporter gene. In addition, a chromatin immunoprecipitation assay further confirmed that BDE-99 could bind to the AhR and activate the AhR nuclear translocation and dioxin responsive element (DRE) binding in the context of the CYP1A1 promoter. However, the transactivation function of the BDE-99-activated AhR seems to be very weak. These combined results suggest that PBDEs do bind but not activate the AhR-AhR nuclear translocator protein-XRE complex.     

Application of the ethoxyresorufin-O-deethylase (EROD) assay to mixtures of halogenated aromatic compounds

The ethoxyresorufin-O-deethylase (EROD) assay monitors the induction of the xenobiotic-metabolizing enzyme cytochrome P-450 (CYP) 1A1 and is a widely used biomarker for exposure of wildlife to substances that bind the aryl hydrocarbon (Ah) receptor. In this work the induction of EROD activity by single compounds and binary mixtures in primary rat hepatocytes was compared with the predictions of a kinetic model involving mixtures of inducers. The inducing agents were also examined for their ability to activate the Ah receptor to its DNA-binding form and for their ability to act as competitive inhibitors for CYP 1A1. Xenobiotics that failed to activate the Ah receptor did not induce EROD activity. Competitive inhibition for CYP 1A1 between the xenobiotic and 7-ethoxyresorufin caused EROD activity to fall at high xenobiotic concentrations. Competition for a limited number of Ah receptor sites depressed the EROD activity of a strong inducer such as 2,3,7,8-tetrachlorodibenzo-p-dioxin at high concentrations of a weak inducer. Application of the kinetic model to the example of a mixture of low concentrations of dibenzo-p-dioxins and much higher concentrations of polychlorinated biphenyls indicated that EROD assays often seriously underestimate the true potency of an environmental sample. Hence the EROD assay cannot be used for determining dioxin equivalent concentrations using the toxic equivalence factor approach.