Induction of cytochrome P450-dependent monooxygenase activities in rat hepatoma H-4-IIE cells in culture by 2,3,7,8-tetrachlorodibenzo-p-dioxin and related compounds: mechanistic studies using radiolabeled congeners

Use of [125I]4'-iodoflavone as a tool to characterize ligand-dependent differences in Ah receptor behavior

We have synthesized [(125)I]4'-iodoflavone to study Ah receptor (AhR)-ligand interactions by a class of AhR ligands distinct from the prototypic ligand 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). This radioligand allows the comparison of AhR-ligand interactions using a ligand that differs in AhR affinity, and yet has the same radiospecific activity as [(125)I]2-iodo-7,8-dibromodibenzo-p-dioxin. Specific binding of [(125)I]4'-iodoflavone with the AhR was detected as a single radioactive peak ( approximately 9.7 S) following density sucrose gradient analysis. Cytosolic extracts from both Hepa 1 and HeLa cells were used as the source of mouse and human AhR, respectively. A approximately 6.7 S form of radioligand-bound Ah receptor was detected in the high salt nuclear extracts of both cell lines. In HeLa cells approximately twofold more [(125)I]4'-iodoflavone-AhR 6 S complex, compared with [(125)I]2-iodo-7,8-dibromodibenzo-p-dioxin, was recovered in nuclear extracts. A comparison of the ability of 4'-iodoflavone and TCDD to cause time-dependent translocation of AhR-yellow fluorescent protein revealed that 4'-iodoflavone was more efficient at enhancing nuclear accumulation of the receptor. These results suggest that [(125)I]4'-iodoflavone is a particularly useful and easily synthesized ligand for studying the AhR.

Basis for a proposed reference dose (RfD) for dioxin of 1-10 pg/kg-day: a weight of evidence evaluation of the human and animal studies

The dioxins have been perhaps the most studied of all chemicals to which humans are routinely exposed. It has been reported that more than 5,000 scientific papers have been published that have evaluated the toxicology of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Although the cancer hazard posed by this chemical has probably received the bulk of attention over the past 20 years, the U.S. Environmental Protection Agency (EPA) and the recent U.S. EPA Science Advisory Board (SAB) that reviewed the "Reassessment" have suggested that the noncancer hazard may well be more important than the cancer hazard at current background doses to the general public. The World Health Organization (WHO) and U.K. Food Standards Agency (FAO) committee (JECFA) on dioxins has reached similar conclusions. This article reviews the published studies involving laboratory animals and humans that address the noncancer effects. Based on our review, developmental toxicity is the most sensitive effect of TCDD consistently seen in mice and rats. Specifically, of the various studies, a no-observed-adverse-effects level (NOAEL) of 13 ng/kg (maternal body burden) was identified as the most pertinent for deriving a reference dose (RfD) for humans. Although more than a dozen different adverse effects have been reported in various studies of humans over the past 25 years, the most consistent clinically important adverse effect of human exposure appears to be chloracne. Following a review of all published studies, we concluded that the best estimate of a LOAEL for production of chloracne is approximately 160 ng/kg (body burden). Based on our analysis, an RfD of between 1 and 10 pg/kg-d (TCDD TEQ) is consistent with the objectives of this risk criterion. Maintaining a lifetime average daily dose below this concentration, based on what is known today, should prevent noncancer effects in virtually all persons. This value is consistent with the JECFA recommendation of 70 pg/kg-mo.

Combinatorial bio/chemical analysis of dioxin and dioxin-like compounds in waste recycling, feed/food, humans/wildlife and the environment

The present review describes international activities using bioassays/biomarkers in combination with chemical analysis to measure the effects of dioxin and dioxin-like compounds (DLCs) in the environment. The above authors reviewed already the state-of-art bioanalytical detection methods (BDMs) for dioxins and DLCs [Environ Int (2001)]. The aim of this study will be to review applications of these bioassays/biomarkers to evaluate potential dioxins and DLCs. The present literature study lists relative potencies (REPs) of polyhalogenated dibenzo-p-dioxins and -furans (PXDD/Fs; X = Cl, Br, F), their thio analogues polychlorinated dibenzothiophenes (PCDTs) and thianthrens (PCTAs), polyhalogenated biphenyls (PXBs), polychlorinated naphthalenes (PCNs) and other Ah receptor agonists measured by several biodetectors (Tier 3 screening). The authors will discuss some examples of the applications of some of these biodetectors in biomonitoring programmes and recently occurred dioxin crisis in feed/food. The diagnosis of the biopotency of these pollutants in technical processes like thermally treated waste, waste water treatment, landfill leachate treatment, commercial PCB-mixtures, the release into the environment (soil, air and water) and the final intake into wildlife and humans will be reviewed.

Bioanalytical screening methods for dioxins and dioxin-like compounds a review of bioassay/biomarker technology

Determination of environmental pollutants utilizing biodetectors such as bioassays, biomarkers, enzyme immunoassays (EIAs), or other bioanalytical tools is a continuously growing area. The present literature review describes the principles and advantages/limitations of several bioanalytical detection methods (BDMs) for the screening and diagnosis of dioxin and dioxin-like compounds. This study characterizes briefly the family of dioxin and dioxin-like compounds, discusses potential Ah receptor (AhR) ligands and cytochrome P-450 (CYP) 1A1-enzyme-inducing compounds. 'Milestones' in the development of BDMs are summarized and explained in detail for a number of bioanalytical tools that can be used to detect these classes of dioxin-like persistent bioaccumulative toxicants (PBTs). The design of a screening profile with a battery of bioassays/biomarkers coupled with the chemical analysis is evaluated. The relative potencies (REPs) to 2,3,7,8-TCDD for dioxin-like compounds are reviewed for various BDMs and the differences are noted.

Competitive inhibition by inducer as a confounding factor in the use of the ethoxyresorufin-O-deethylase (EROD) assay to estimate exposure to dioxin-like compounds

The ethoxyresorufin-O-deethylase (EROD) assay has been extensively used in whole animals and in cell culture as a biomarker of exposure to environmental contaminants such as dioxin-like compounds (DLCs). This paper addresses two controversial phenomena that arise when DLCs are examined by the EROD assay. Firstly, the maximum level of induced EROD activity varies with the identity of the inducing compound; secondly, the induced EROD activity reaches a concentration-dependent maximum level that is followed by an apparent reduction in activity when the concentration of inducer is further increased. These phenomena are completely explained by competitive inhibition of the EROD enzyme-substrate reaction by the dioxin-like compound. A kinetic model explains the biphasic appearance of EROD induction curves as a function of a compound's binding affinity with the Ah receptor (Kd) and its binding affinity to CYP 1A1 (Ki) which results in inhibition of the EROD enzyme-substrate reaction. These results limit the reliability of the information obtained from calibration curves of EROD activity versus concentration of a standard DLC such as 2,3,7,8-tetrachlorodibenzo-p-dioxin.

Estrogen does not inhibit 2,3,7, 8-tetrachlorodibenzo-p-dioxin-mediated effects in MCF-7 and Hepa 1c1c7 cells

The estrogen receptor and aryl hydrocarbon receptor (AhR) are coexpressed in several Ah and estrogen-responsive human breast cancer cell lines. However, a recent study reported that 17beta-estradiol (E2) inhibited Ah responsiveness in mouse Hepa 1c1c7 hepatoma cells (Kharat, I., and Saatcioglu, F. (1996) J. Biol. Chem. 271, 10533-10537), and therefore, estrogen receptor-AhR cross-talk was reinvestigated in MCF-7 and mouse Hepa 1c1c7 cells. Treatment of MCF-7 or Hepa 1c1c7 cells with 2,3,7, 8-tetrachlorodibenzo-p-dioxin (TCDD) resulted in induction of CYP1A1-dependent activity and mRNA levels. Treatment of both cell lines with E2 had no effect on basal or TCDD-inducible CYP1A1-dependent activity or mRNA levels. In MCF-7 and Hepa 1c1c7 cells transiently transfected with an Ah-responsive plasmid containing the 5'-regulatory region of the human CYP1A1 gene fused to the chloramphenicol acetyltransferase reporter gene 10 nM TCDD significantly induced chloramphenicol acetyltransferase activity; in cells cotreated with TCDD plus E2 the induced response was not affected by the hormone. Nuclear extracts from cells treated with dimethyl sulfoxide, E2, TCDD, and TCDD plus E2 were incubated with the [32P]dioxin-responsive element and analyzed by gel electrophoretic mobility shift assays. A retarded band associated with formation of a [32P]dioxin-responsive element-AhR complex was observed in nuclear extracts from cells treated with TCDD or TCDD plus E2 (cotreated). Collectively these studies suggest that E2 does not modulate AhR-mediated CYP1A1 gene expression in MCF-7 or Hepa 1c1c7 cells.

Substituted flavones as aryl hydrocarbon (Ah) receptor agonists and antagonists

The structure-dependent aryl hydrocarbon (Ah) receptor agonist and antagonist activities of the following substituted flavones were investigated: flavone, 4'-methoxy-, 4'-amino-, 4'-chloro-, 4'-bromo-, 4'-nitro-, 4'-chloro-3'-nitro-, 3'-amino-4'-hydroxy-, 3',4'-dichloro-, and 4'-iodoflavone. The halogenated flavones exhibited competitive Ah receptor binding affinities (IC50 = 0.79 to 2.28 nM) that were comparable to that observed for 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) (1.78 nM). The compounds also induced transformation of the rat cytosolic Ah receptor and induced CYP1A1 gene expression in MCF-7 human breast cancer cells. However, despite the high Ah receptor binding affinities for these responses, the halogenated flavones were > 1000 times less active than TCDD for the other responses. Moreover, for other substituted flavones, there was no correlation between Ah receptor binding affinities and their activities as Ah receptor agonists. For example, 4'-aminoflavone induced CYP1A1 mRNA levels in MCF-7 cells but exhibited relatively low Ah receptor binding affinity (IC50 = 362 nM) and did not induce transformation of the rat cytosolic Ah receptor. All of the substituted flavones inhibited TCDD-induced transformation of the Ah receptor, and 4'-iodoflavone, an Ah receptor agonist at high concentrations (1-50 microM), inhibited the transformation at concentrations as low as 0.05 and 0.5 microM. Subsequent interaction studies with TCDD and 4'-iodoflavone confirmed that the latter compound inhibits induction of CYP1A1 gene expression by TCDD in MCF-7 cells. The results obtained for the substituted flavones suggest that within this structural class of compounds, various substituent groups can affect markedly the activity of each individual congener as an Ah receptor agonist or antagonist. These substituent-dependent differences in activity may be related to ligand-induced conformational changes in the Ah receptor complex and/or support the proposed existence of more than one form of the Ah receptor.

In vitro inhibition of 2,3,7,8-tetrachlorodibenzo-p-dioxin-induced activity by alpha-naphthoflavone and 6-methyl-1,3,8-trichlorodibenzofuran using an aryl hydrocarbon (Ah)-responsive construct

Rat hepatoma H4IIE and mouse hepatoma Hepa 1c1c7 cells were transiently transfected with a plasmid construct that contained the bacterial chloramphenicol acetyltransferase (CAT) gene under the control of the mouse mammary tumor virus promoter and one copy of the dioxin responsive element. Treatment of transfected H4IIE and Hepa 1c1c7 cells with 10(-13) to 10(-6) M 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) resulted in a concentration-dependent increase in transient CAT activity. Maximum CAT activity was induced in both cell lines by exposure to 10(-9) M TCDD. The induction of CAT activity correlated well with the TCDD-induced, P4501A1-dependent ethoxyresorufin O-deethylase activity. Cotreatment of transfected cells with 10(-9) M TCDD and 10(-8) to 10(-6) M alpha-naphthoflavone (alpha NF) or 6-methyl-1,3,8-trichlorodibenzofuran (MCDF) resulted in a concentration-dependent reduction of TCDD-induced CAT activity. Treatment of cells with 10(-6) M alpha NF or MCDF alone resulted in only minimal induction of CAT activity. Both antagonists inhibited the induction of genes under the control of the CYP1A1 and mouse mammary tumor virus promoters, which indicates that the alpha NF- and MCDF-mediated antagonism of TCDD-induced, aryl hydrocarbon receptor-dependent gene transcription does not depend on promoter context.

Modulation of gene expression and endocrine response pathways by 2,3,7,8-tetrachlorodibenzo-p-dioxin and related compounds

The aryl hydrocarbon (Ah) receptor binds several different structural classes of chemicals, including halogenated aromatics, typified by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), polynuclear aromatic and heteropolynuclear aromatic hydrocarbons. TCDD induces expression of several genes including CYP1A1, and molecular biology studies show that the Ah receptor acts as a nuclear ligand-induced transcription factor that interacts with xenobiotic or dioxin responsive elements located in 5'-flanking regions of responsive genes. TCDD also elicits diverse toxic effects, modulates endocrine pathways and inhibits a broad spectrum of estrogen (17 beta-estradiol)-induced responses in rodents and human breast cancer cell lines. Molecular biology studies show that TCDD inhibited 17 beta-estradiol-induced cathepsin D gene expression by targeted interaction of the nuclear Ah receptor with imperfect dioxin responsive elements strategically located within the estrogen receptor-Sp1 enhancer sequence of this gene.

Comparative kinetic study of the binding between 2,3,7,8-tetrachlorodibenzo-p-dioxin and related ligands with the hepatic Ah receptors from several rodent species

Kinetic analysis of the time course of association of [3H]-2,3,7,8-tetrachlorodibenzo-p-dioxin with hepatic cytosol from five rodent species gave additional evidence for differences in the properties of the Ah receptor ligand binding subunit between species. A parallel study of the association of six tritiated polychlorinated dibenzo-p-dioxins and dibenzofurans with hepatic Ah receptor from Wistar rat and C57BL/6 mouse showed that their rank order for kinetic affinity did not correlate with the rank ordering of their toxic potency and may vary according to the source of the Ah receptor.

Mechanism of action of aryl hydrocarbon receptor antagonists: inhibition of 2,3,7,8-tetrachlorodibenzo-p-dioxin-induced CYP1A1 gene expression

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) induces CYP1A1 gene expression as determined by increased CYP1A1 mRNA levels and ethoxyresorufin O-deethylase (EROD) activity in mouse Hepa 1c1c7, rat hepatoma H-4II E and human Hep G2 cancer cell lines. In contrast, treatment of these cell lines with either alpha-naphthoflavone (alpha NF) or 6-methyl-1,3,8-trichlorodibenzofuran (MCDF) at concentrations as high as 10(-6) M resulted in only minimal induction of CYP1A1 mRNA levels or EROD activity. Cotreatment of the cells with 10(-9) M TCDD plus different concentrations (10(-8)-10(-6) M) of MCDF or alpha NF resulted in a concentration-dependent decrease in TCDD-induced CYP1A1 mRNA levels and EROD activity in the three cell lines. Moreover, using 10(-9) M [3H]TCDD, it was shown that the alpha NF- and MCDF-mediated antagonism of TCDD-induced CYP1A1 gene expression was paralleled by a decrease in levels of the nuclear [3H]TCDD-Ah receptor complex as determined by velocity sedimentation analysis of the nuclear extracts. The binding of nuclear extracts from the treated cells to a synthetic consensus dioxin responsive element (DRE) (a 26-mer) was determined by gel retardation studies using 32P-DRE. In cells treated with 10(-9) M TCDD or TCDD plus 10(-8)-10(-6) M alpha NF, the concentration-dependent decrease in TCDD-induced CYP1A1 gene expression by alpha NF was also paralleled by decreased levels of a retarded band associated with the nuclear Ah receptor-DRE complex. In contrast, the results of the gel shift assay of nuclear extracts treated with 10(-9) M TCDD or TCDD plus 10(-8)-10(-6) M MCDF indicated that there were relatively high levels of nuclear MCDF-Ah receptor complex in the cells co-treated with TCDD plus the antagonist but this was not accompanied by induced CYP1A1 gene expression. The results suggest that alpha NF and possibly MCDF compete with TCDD for cytosolic Ah receptor binding sites; however, MCDF may also inhibit the induction response by competing for and/or partially inactivating genomic binding sites.

Effects of ligand structure on the in vitro transformation of the rat cytosolic aryl hydrocarbon receptor

Incubation of radiolabeled, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,7,8-tetrachlorodibenzofuran (TCDF),1,2,3,7,8-pentachlorodibenzo-p-dioxin(PeCDD), 1,2,3,7,8-pentachlorodibenzofuran (PeCDF), 1,2,7,8-TCDF, and 2,3,7-trichlorodibenzo-p-dioxin (TrCDD) with rat hepatic cytosol for 2 h at 0 degrees C gave liganded aryl hydrocarbon (Ah) receptor complexes which were indistinguishable as determined by velocity sedimentation analysis and DNA-Sepharose column chromatography. Incubation of the cytosol plus the different radioligands for 2 h at 20 degrees C resulted in the formation of Ah receptor complexes which exhibited increased retention times on DNA-Sepharose columns. It was apparent that the amount of specifically bound Ah receptor complex or the levels of the transformed Ah receptor complex which eluted from the column with 0.2-0.3 M salt were dependent on the structure of the radioligand. For example, after incubation for 2 h at 20 degrees C the overall yields of the specifically bound transformed Ah receptor complex were 3.4, 2.0, 1.2, 1.9, 0.3, and 0.1%, respectively, using 2,3,7,8-TCDD, 2,3,7,8-TCDF, 1,2,3,7,8-PeCDD, 1,2,3,7,8-PeCDF, 1,2,7,8-TCDF, and 2,3,7,8-TrCDD as radioligands. A more quantitative measure of the structure-dependent transformation of the liganded cytosolic Ah receptor complex was determined using a gel retardation assay with a consensus synthetic dioxin-responsive element (DRE) (26-mer, duplex). The EC50 values obtained for the concentration-dependent formation of the retarded DRE-Ah receptor complex using 2,3,7,8-TCDD, 1,2,3,7,8-PeCDD, 2,3,7,8-TCDF, 1,2,3,7,8-PeCDF, 2,3,7-TrCDD, and 1,2,7,8-TCDF as ligands were 0.26, 0.35, 0.78, 1.75, 27.0, and 220 nM, respectively. The structure-dependent differences in these values were similar to their different potencies as Ah receptor agonists and these data suggest that the structure-dependent transformation of the liganded cytosolic Ah receptor may significantly contribute to the structure-activity relationships observed for 2,3,7,8-TCDD and related compounds.

Recent developments on the hazards posed by 2,3,7,8-tetrachlorodibenzo-p-dioxin in soil: implications for setting risk-based cleanup levels at residential and industrial sites

Since the publication of the Times Beach risk assessment in 1984, which suggested that residential soils were of concern when the level of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was in excess of 1 ppb, there has been continued interest in this topic. Studies conducted within the past 5 yr on the environmental and toxicological behavior of TCDD, as well as refinement of parameters regarding human exposure, indicate that previous assessments of the risk to humans posed by TCDD-contaminated soil were overestimated. In this paper, recent information drawn from nearly 100 recently published articles regarding the histopathology interpretation of the Kociba bioassay, environmental fate and half-life of TCDD in soil, and estimates of human exposure via soil ingestion, dermal contact, inhalation, surface runoff, and the consumption of fish were incorporated into a risk assessment. Cleanup levels for TCDD in residential and industrial soils were calculated based on most likely exposure scenarios. Probability distributions of key exposure parameters were incorporated into a Monte Carlo uncertainty analysis to predict the range and probability of TCDD uptake and corresponding cleanup levels in soil. This analysis demonstrated that the most significant route of human exposure to TCDD is through dermal contact with soil, followed by soil ingestion, fish consumption, and inhalation of airborne particulates. At residential sites, soils containing 20 parts per billion (ppb) of TCDD were found to pose a lifetime cancer risk no greater than 1 in 100,000 (10(-5) risk) under typical exposure conditions. Based on the Monte Carlo analysis, soil concentrations for the 75th and 95th percentile person were 12 and 7 ppb (10(-5) risk), respectively. In industrial soils, TCDD concentrations ranged between 131 and 582 ppb (10(-5) risk), depending on the amount of time spent outdoors under typical exposure conditions. Industrial soil concentrations of approximately 93 and 46 ppb (10(-5) risk) were calculated for the 75th and 95th percentile worker, respectively, engaged in outdoor activities. The range of TCDD concentrations in industrial soils was not reduced significantly when the consumption of fish from a neighboring waterway by off-site receptors was considered. While cleanup levels for TCDD should be derived on a site-specific basis, this analysis indicated that soil cleanup standards can be generally higher than those implemented over the past 8 yr.

Characterization of the aryl hydrocarbon receptor in the human C-4II cervical squamous carcinoma cell line

Treatment of C-4II human cervical squamous carcinoma cells with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) gave a concentration-dependent increase in ethoxyresorufin O-deethylase (EROD) activity. The EC50 for this response was approximately 1 nM and the maximum induced activity was 27 pmol/min/mg protein. The molecular properties of the cytosolic and nuclear aryl hydrocarbon (Ah) receptor complex were determined by velocity sedimentation analysis, photoaffinity labeling, gel retardation using a consensus dioxin responsive element (DRE), and DNA-Sepharose, DRE-Sepharose and Sephacryl S-300 gel permeation column chromatography. The apparent molecular masses of the cytosolic and nuclear photoaffinity-labeled Ah receptor complexes were 110 kDa and differed from the corresponding values obtained for the Ah receptor from other animal species. In contrast, most of the other molecular properties of the Ah receptor were not significantly different from those previously reported for other species. The relative Ah-responsiveness of the C-4II cells was assessed by determining the ratio of the induced EROD activity/nuclear Ah receptor levels for a submaximal inducing dose of [3H]TCDD. The induced activity/binding ratio for the human C-4II cells was 0.77 and was at least one order of magnitude lower than the corresponding value for the Ah-responsive rat hepatoma H-4-II E cells.

Induction of CYP1A1 gene expression in H4-II-E rat hepatoma cells by benzo[e]pyrene

In the rat, expression of the CYP1A1 gene is closely associated with arylhydrocarbon hydroxylase (AHH) enzyme activity. AHH is an inducile enzyme activity known to play an important role in the bioactivation of polycyclic aromatic hydrocarbons (PAHs) to mutagenic and carcinogenic metabolites. PAH-induced expression of the CYP1A1 gene appears to be regulated by several trans-acting factors, including the Ah receptor and the 4S PAH-binding protein. In this study, we used the PAH isomers benzo[a]pyrene (BaP) and benzo[e]pyrene (BeP) to further evaluate the role of the 4S PAH-binding protein in induction of the CYP1A1 gene in H4-II-E rat hepatoma cells. Although BaP is believed to bind to both the Ah receptor and the 4S protein, BeP has been reported to bind exclusively to the 4S protein. The results of the study presented here indicate that BaP and BeP induce the expression of the CYP1A1 gene, as measured by ethoxyresorufin O-deethylase (EROD) activity, in a concentration-dependent manner. However, BaP is about 25 times as potent as BeP in inducing EROD activity in these cells. Slot-blot analysis of total RNA isolated from these cells indicated that BeP, BaP, and 3-methylcholanthrene increased the level of CYP1A1 mRNA expression. Sucrose-gradient analysis of BeP binding activity indicated that BeP bound with high affinity to the 4S PAH-binding protein, but not to the Ah receptor. These results suggest that the 4S protein may play a role in the PAH-induced expression of the CYP1A1 gene in rat H4-II-E cells.

In situ and in vitro photoaffinity labeling of the nuclear aryl hydrocarbon receptor from transformed rodent and human cell lines

The photoaffinity labeling of the nuclear aryl hydrocarbon (Ah) receptor from mouse Hepa 1c1c7, rat hepatoma H-4-II E, and human liver Hep G2 cells was investigated using two high affinity ligands, namely 2,3,7,8-[3H]tetrachlorodibenzo-p-dioxin (TCDD) and 7-[125I]iodo-2,3,-dibenzo-p-dioxin ([125I]DBDD). Irradiation of nuclear [3H]TCDD-Ah receptor complexes from the three cell lines for 5 min gave 47, 38, and 62% yields of trichloroacetic acid-precipitable photoadducts from the Hepa 1c1c7, H-4-II E, and Hep G2 cell lines, respectively; denaturing sodium dodecyl sulfate-polyacrylamide gel electrophoresis separation followed by autoradiography gave one major Ah receptor photoadduct for each cell line with apparent molecular masses at 97, 100, and 110 kDa, respectively. [125I]DBDD could also be used as a photoaffinity label for the nuclear Ah receptor from the three cell lines; although the maximum net yield of photoaffinity labeled nuclear Ah receptor from the rodent nuclear Ah receptor preparations was relatively low (0.5-2.5%), a greater than 15% yield of photoadduct was obtained from the human Hep G2 cells. Both [3H]TCDD and [125I]DBDD were utilized to photoaffinity label the nuclear Ah receptor in Hepa 1c1c7 cells in suspension and the net yield of photoadducts with these ligands was 94.6 and 3.0%, respectively. The cytosolic Ah receptor from the three cell lines was photolabeled with [125I]DBDD and the net yield of photoadducts varied from 3.3 to 14.7%. The functional activity of the photoaffinity-labeled nuclear TCDD-Ah receptor complexes from the cell lines was also determined by comparing relative binding affinities of the photolyzed and unphotolyzed complexes with a synthetic dioxin-responsive element (DRE) using a gel retardation assay. The photolyzed and unphotolyzed complexes from the three cell lines all bound with the DRE in the gel shift assay; however, the gel mobilities of the rodent and human nuclear receptor-DRE complexes were different. Quantitative analysis of the DRE binding showed that there were no significant differences between the photolyzed and unphotolyzed nuclear receptor complexes from the rodent cells, whereas there was a significant 27% decrease in the DRE binding of the photolyzed versus the unphotolyzed nuclear receptor complex from the human Hep G2 cells. These studies demonstrate the utility of [3H]TCDD and [125I]DBDD as photoaffinity labels for the Ah receptor and illustrate the structural and photochemical differences between the rodent and the human nuclear Ah receptor complexes.

Mechanism of action of 2,3,7,8-tetrachlorodibenzo-p-dioxin antagonists: characterization of 6-[125I]methyl-8-iodo-1,3-dichlorodibenzofuran-Ah receptor complexes

6-Methyl-8-iodo-1,3,-dichlorodibenzofuran (I-MCDF) and its radiolabeled analog [125I]MCDF have been synthesized and used to investigate the mechanism of action of 1,3,6,8-substituted dibenzofurans as 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) antagonists. Like 6-methyl-1,3,8-trichlorodibenzofuran (MCDF), I-MCDF partially antagonized the induction by TCDD of microsomal aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) activities in rat hepatoma H-4-II E cells and male Long-Evans rat liver. Incubation of rat liver cytosol with [125I]MCDF followed by velocity sedimentation analysis on sucrose gradients gave a specifically bound peak which sedimented at 9.6 S. This radioactive peak was displaced by coincubation with a 200-fold excess of unlabeled I-MCDF, 6-methyl-1,3,8-trichlorodibenzofuran (MCDF), 2,3,7,8-tetrachlorodibenzofuran (TCDF), and benzo [a]pyrene. Based on the velocity sedimentation results and the elution profile from a Sephacryl S-300 gel permeation column, the Stokes radius and apparent molecular weights of the cytosolic [125I]MCDF-Ah receptor complex were 6.5 nm and 259,200, respectively. In addition, the nuclear [125I]MCDF-receptor complex eluted at a salt concentration of 0.29 M KCl from a DNA-Sepharose column. Velocity sediment analysis of the nuclear [125I]MCDF-Ah receptor complex from rat hepatoma H-4-II E cells gave a specifically bound peak at 5.6 +/- 0.8 S. All of these properties were similar to those observed using [3H]TCDD as the radioligand. In addition, there were several ligand-dependent differences observed in the properties of the I-MCDF and TCDD receptor complexes; for example, the [125I]MCDF rat cytosolic receptor complex was unstable in high salt buffer and was poorly transformed into a form with increased binding affinity on DNA-Sepharose columns; Scatchard plot analysis of the saturation binding of [3H]TCDD and [125I]MCDF with rat hepatic cytosol gave KD values of 1.07 and 0.13 nM and Bmax values of 137 and 2.05 fmol/mg protein, respectively. The nuclear extract from rat hepatoma H-4-II E cells treated with I-MCDF or TCDD interacted with a dioxin-responsive element in a gel retardation assay. These results suggest that the mechanism of antagonism may be associated with competition of the antagonist receptor complex for nuclear binding sites.

Production of Ah receptor ligands in rat fecal suspensions containing tryptophan or indole-3-carbinol

An assay system was developed to test whether bacteria in the gastrointestinal tract are capable of metabolizing tryptophan to compounds that are able to bind to the aryl hydrocarbon (Ah) receptor. Tryptophan (1 mM) was added to feces diluted 1:1,000 in phosphate-buffered saline and incubated at 37 degrees C overnight. The suspensions were extracted with chloroform to obtain the hydrophobic compounds. To test for the presence of Ah receptor ligands, a competition binding assay using [2-125I]iodo-7, 8-dibromodibenzo-p-dioxin and Hepa 1c1c7 cytosol was employed; it was capable of detecting picogram levels of a competing ligand with similar affinity. Fecal suspensions in the presence of 1 mM tryptophan and oxygen are capable of producing greater than 60% inhibition of radioligand binding per 10 micrograms of feces. In contrast, oxygen-equilibrated fecal suspensions without tryptophan and argon-equilibrated fecal suspensions with tryptophan exhibited 10% inhibition of radioligand binding per 10 micrograms of feces in the competition binding assay. Other indolylic compounds and amino acids were similarly tested. Histidine, tyrosine, phenylalanine, glycine, indole-3-acetic acid, and tryptamine were all negative in this assay. Indole-3-carbinol was capable of forming compounds that bind to the Ah receptor under a variety of conditions: in fecal suspensions with or without oxygen, in 50 mM HCl for 80 minutes, and in neutral pH buffer overnight at 37 degrees C. Addition of oxygenated tryptophan-fecal incubation extracts to Hepa 1 and Hepa c4 mutant (defective Ah receptor) cell cultures resulted in the induction of ethoxyresorufin O-deethylase activity in Hepa 1 cells, but no induction was observed in Hepa c4 cells. These results suggest that bacteria in the gastrointestinal tract under the proper conditions are able to metabolize tryptophan to compounds that are Ah receptor ligands.

Structure-dependent induction of aryl hydrocarbon hydroxylase activity in C57BL/6 mice by 2,3,7,8-tetrachlorodibenzo-p-dioxin and related congeners: mechanistic studies

The time- and dose-dependent induction of murine hepatic microsomal aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) activities by five polychlorinated dibenzo-p-dioxin and dibenzofuran congeners showed that the order of induction potency was 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) greater than 2,3,7,8-tetrachlorodibenzofuran (TCDF) greater than 1,2,3,7,8-pentachlorodibenzo-p-dioxin (PCDD) greater than 1,2,3,7,8-pentachlorodibenzofuran (PCDF) greater than 2,3,7-trichlorodibenzo-p-dioxin (TrCDD). These structure-induction relationships were comparable to the structure-toxicity and competitive structure-receptor binding relationships previously reported for these compounds. However, using the corresponding radiolabeled congeners, the direct binding Kd values for dissociation of the cytosolic receptor-ligand complexes were 9.52, 7.96, 1.27, 3.10, and 8.31 nM for the 2,3,7,8-TCDD, 2,3,7,8-TCDF, 2,3,7-TrCDD, 1,2,3,7,8-PCDD, and 1,2,3,7,8-PCDF congeners and these data were clearly not structure dependent (i.e., similar to the structure-activity relationships). Some of the molecular properties for several radioligand-receptor complexes were similar; for example, the sedimentation coefficients for the cytosolic and nuclear receptor complexes varied from 8.8-10.4 S and 5.98-7.0 S, respectively, and the nuclear receptor complexes for all the radioligands eluted from a DNA-Sepharose column at salt concentrations of 0.27-0.29 M. Treatment of the mice with a maximum inducing dose of 2,3,7,8-[3H]TCDD resulted in a time-dependent formation of the nuclear receptor complex which was maximized between 16-24 hr and subsequently decreased up to 72 hr after initial exposure. In parallel studies, the nuclear receptor complex levels were determined 16 hr after treatment of the mice with different doses (2.25, 4.5, and 45 micrograms/kg) of all five radioligands. The results showed that at submaximal induction of the monooxygenase enzyme activities there was a linear correlation between the induced AHH or EROD activities (after 32 hr) and the corresponding nuclear receptor complex levels. It was also apparent from the data that the relative levels of nuclear receptor complex were structure dependent and this suggests that the transformation or activation of cytosolic receptor complexes may be a ligand structure-dependent process which correlates with the observed structure-activity relationships for 2,3,7,8-TCDD and related compounds.

The mechanism of action of alpha-naphthoflavone as an inhibitor of 2,3,7,8-tetrachlorodibenzo-p-dioxin-induced CYP1A1 gene expression

Treatment of rat hepatoma H-4-II E cells with alpha-naphthoflavone (alpha NF) (10(-8), 10(-7), 10(-6)M) resulted in only minimum induction of ethoxyresorufin O-deethylase (EROD) activity and cytochrome P4501A1 mRNA levels only at 10(-6)M. In contrast, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) caused maximum or near maximum induction responses at 10(-8) and 10(-9)M. In a time-course study with TCDD (10(-9)M), and TCDD plus alpha NF (cotreated), alpha NF significantly inhibited the induction of EROD activity and cytochrome P4501A1 mRNA levels by TCDD for 6-24 h after initial exposure of the cells to the chemicals. In addition, treatment of the cells with 10(-9)M TCDD in the presence or absence of 10(-8), 10(-7), and 10(-9)M alpha NF showed that the latter compound inhibited the induction effects by TCDD in a concentration-dependent manner and these inhibitory effects could be overcome, in part, by a higher concentration of TCDD (10(-8)M). Treatment of the rat hepatoma H-4-II E cells with [3H]TCDD showed that within 60 min, there was an initial rapid increase in nuclear [3H]TCDD receptor complex levels (38 fmol/mg protein) which decreased to less than 10 fmol/mg protein within 4 h and remained relatively constant for up to 24 h. However, in cells treated with [3H]TCDD (10(-9)M) plus alpha NF (10(-6)M) the levels of the nuclear [3H]TCDD receptor complex were less than 5 fmol/mg protein throughout the 24-h time course. These data, coupled with the results which indicate that the alpha NF competitively inhibits the binding of [3H]-TCDD to the cytosolic aryl hydrocarbon (Ah) receptor, suggest that alpha NF inhibits the TCDD-mediated induction of CYP1A1 gene transcription and translation by direct competition for cytosolic Ah receptor binding sites.

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.