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S Safe

Publications and source records attributed to S Safe.

At least 145 records · Page 8Linked to original sources

Development of bioassays and approaches for the risk assessment of 2,3,7,8-tetrachlorodibenzo-p-dioxin and related compounds.

Polychlorinated biphenyls (PCBs), dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and related halogenated aromatic hydrocarbons (HAHs) are industrial compounds or by-products that have been identified as contaminants in almost every component of the global ecosystem. 2,3,7,8- Tetrachlorodibenzo-p-dioxin (TCDD) is the most toxic HAH, and studies in rodents have shown that this compound is a carcinogen. Analysis of environmental samples for HAHs has shown that these extracts contain complex mixtures of isomers and congeners, and this greatly complicates risk assessment due to the paucity of data available for most of the individual compounds. Extensive research has demonstrated a common receptor-mediated mechanism of action for TCDD and related toxic HAHs, and this has led to the development of a mechanism-based risk assessment approach for HAHs. Toxic equivalency factors (TEFs; relative potency compared to TCDD) have been developed for selected HAH congeners, and the TEF values can be used to determine "toxic equivalents" (TEQs) for HAH mixtures. In addition, several bioassays that use receptor-mediated end points have been developed and can be used directly to determine the TEQs for HAH mixtures. The applications of the TEF/TEQ approach for the risk assessment of HAHs are considerable, particularly with the conversion of complex analytical data into TEQs. However, there appear to be several limitations to this approach, particularly with PCBs because their potential nonadditive (antagonistic), interactive effects with "2,3,7,8-TCDD-like" compounds may invalidate the use of the risk assessment procedure for some environmental matrices.

Benzofurans↗

alpha-Naphthoflavone-induced CYP1A1 gene expression and cytosolic aryl hydrocarbon receptor transformation.

alpha-Naphthoflavone (alpha NF) is a weak aryl hydrocarbon (Ah) receptor agonist and inhibits the induction of CYP1A1 gene expression by 2,3,7,8-tetrachlorodibenzo-p-dioxin. It has been suggested that the Ah receptor antagonist activity is due to the formation of alpha NF-cytosolic Ah receptor complexes that fail to undergo transformation. This hypothesis is consistent with data obtained in this and other studies using alpha NF concentrations from 10 to 1000 nM. However, 10 microM alpha NF exhibited Ah receptor agonist activity in several assays. Incubation of rat hepatic cytosol with 10 microM alpha NF caused transformation of the Ah receptor, as determined in a gel retardation assay using a 32P-labeled oligonucleotide containing a single dioxin-responsive element (DRE). Incubation of rat hepatoma (H-4-II E) cells with 10 microM alpha NF not only resulted in the induction of CYP1A1 mRNA levels but also increased chloramphenicol acetyltransferase activity from a DRE-containing chloramphenicol acetyltransferase reporter plasmid. Moreover, the DRE-transformed cytosolic Ah receptor complex liganded with either alpha NF or 2,3,7,8-tetrachlorodibenzo-p-dioxin did not undergo significant dissociation at 4 degrees. These data confirm that alpha NF is an Ah receptor agonist and, based on the results of previous studies, exhibits partial antagonist activity via competition for receptor binding sites.

Animals↗

A comparison of the mouse versus human aryl hydrocarbon (Ah) receptor complex: effects of proteolysis.

The differences in the molecular properties of the nuclear aryl hydrocarbon (Ah) receptor from human Hep G2 and mouse Hepa 1c1c7 cells were investigated by time-dependent partial proteolysis with chymotrypsin or trypsin followed by column chromatographic and velocity sedimentation analysis. The sedimentation coefficients, Stokes radii and apparent molecular weights of the untreated human and mouse Ah receptor complexes were similar. Treatment of the nuclear Ah receptor complexes from both cell lines with chymotrypsin for 10 or 60 min gave lower molecular weight proteolytic products which also exhibited comparable molecular properties and salt gradient elution profiles from Sepharose columns linked to DNA. Treatment of the human and mouse nuclear Ah receptor complexes with trypsin (5 micrograms/mg protein) for 10 or 60 min gave a minor low molecular weight (29.7- or 25.7-kDa) proteolysis product which was detected only with the mouse Hepa 1c1c7 Ah receptor complex. The time- and concentration-dependent proteolytic digest maps of the human and mouse Ah receptor were determined using receptor preparations which were photoaffinity labeled with [125I]7-iodo-2, 3-dibromodibenzo-p-dioxin. The human Ah receptor was significantly more resistant to proteolysis by trypsin or chymotrypsin than the mouse Ah receptor. At a low concentration of chymotrypsin (1 microgram/mg protein) the Hepa 1c1c7 receptor was degraded to two lower molecular weight fragments with apparent M(r) values at 71- and 48-kDa whereas the Hep G2 Ah receptor was relatively stable under these conditions. Although the human Ah receptor was more slowly hydrolyzed than the mouse receptor by trypsin, the major photolabeled breakdown products for the Ah receptor from both cell lines were observed at M(r) 48- and 45-kDa. The results of this study demonstrate that there were subtle but significant differences in the human and mouse Ah receptor complex; however, the proteolysis studies suggest that there are common structural features in their ligand binding sites.

Affinity Labels↗

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.

Animals↗

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.

Animals↗

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.

Base Sequence↗

Development of gel staining techniques for detecting the secretion of procathepsin D (52-kDa protein) in MCF-7 human breast cancer cells.

17 beta-Estradiol stimulates the secretion of the 34- and 52-kDa protein (i.e., cathepsin D and procathepsin D, respectively) from MCF-7 human breast cancer cells and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) inhibits this estrogen-stimulated response. A comparison of the effects of 17 beta-estradiol, TCDD, and their combinations on the secretion of these two proteins was determined using four different assay procedures, namely autoradiographic analysis of the 35S-labeled proteins (from [35S]methionine) separated by polyacrylamide gel electrophoresis (PAGE), densitometric analysis of the silver- and double-stained proteins separated by PAGE, and radioimmunoassay of the proteins using commercially available antibodies to the 52-kDa protein. The results showed that the autoradiographic, staining, and radioimmunoassay procedures gave comparable results with only a few minor differences in the relative amounts of the 52-kDa detected in the various treatment groups. In the medium obtained from 17 beta-estradiol-treated cells that was serially diluted, there was an excellent linear correlation for the relative concentrations of the 52-kDa protein using the double-staining/densitometric procedure and the radioimmunoassay. These results indicate that the double- or silver-staining method may be a useful and rapid method for screening new compounds as antiestrogens in MCF-7 cells.

Autoradiography↗

Mechanism of benzo[a]pyrene-induced Cyp1a-1 gene expression in mouse Hepa 1c1c7 cells: role of the nuclear 6 s and 4 s proteins.

Treatment of wild-type (wt) aryl hydrocarbon (Ah)-responsive mouse Hepa 1c1c7 cells with benzo[a]pyrene (B[a]P) caused a concentration-dependent induction of ethoxyresorufin O-deethylase (EROD) activity. In contrast, B[a]P was inactive as an inducer in Ah nonresponsive class 1 and class 2 mutant cell lines. In parallel experiments, the nuclear fractions from wt cells treated with 10(-7) M [3H]B[a]P contained both the 4 s carcinogen binding protein and the 6 s (Ah receptor) complexes, whereas only the 4 s complex was present in the nuclear fraction of the class 2 mutant cells. The results obtained from cotreatment of wt Hepa 1c1c7 cells with 10(-6) or 10(-7) M B[a]P and 5 x 10(-7) or 10(-7) M 6-methyl-1,3,8-trichlorodibenzofuran (MCDF) showed that MCDF inhibited the induction of EROD activity and Cyp1a-1 mRNA levels by B[a]P. Moreover, using 10(-7) M [3H]B[a]P and unlabeled MCDF, it was shown that MCDF not only inhibited the induction response but also caused a concentration-dependent decrease in levels of the nuclear 6 s complex but not the 4 s complex. In contrast, in situ competition studies with unlabeled 10(-6) M benzo[ghi]-perylene (B[ghi]P) resulted in the elimination of the nuclear [3H]B[a]P 4 s complex (but not the 6 s complex); however, the EROD activity and Cyp1a-1 mRNA levels in cells treated with 10(-7) M B[a]P in the presence or absence of 10(-6) M B[ghi]P were not significantly different. These results indicate that the 4 s binding protein is not required for the induction of Cyp1a-1 gene expression in Hepa 1c1c7 cells and suggest that B[a]P and 2,3,7,8-tetrachlorodibenzo-p-dioxin induce Cyp1a-1 gene expression via a common mechanism which involves binding to the Ah receptor.

Animals↗

The effect of 6-nitro-1,3,8-trichlorodibenzofuran as a partial estrogen in the female rat uterus.

Administration of 6-nitro-1,3,8-trichlorodibenzofuran (6-NCDF) caused a dose- and time-dependent increase in uterine wet weight and cytosolic and nuclear estrogen receptor (ER) and progesterone receptor (PR) levels in immature female Sprague-Dawley rats. These estrogenic effects persisted for up to 96 or 144 hr after initial administration of 6-NCDF and could be observed at a dose as low as 2 mumol/kg. In contrast, 6-NCDF (25 mumol/kg) did not increase rat uterine peroxidase activity or epidermal growth factor (EGF) receptor binding activity. 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD), which exhibits a broad spectrum of antiestrogenic effects in the female rat uterus, inhibited the 17 beta-estradiol-induced increase in uterine wet weights, cytosolic and nuclear ER and PR levels, peroxidase activity, and EGF receptor binding activity. In contrast, 2,3,7,8-TCDD inhibited the uterotropic effects caused by 6-NCDF but did not affect the 6-NCDF-induced uterine ER and PR levels. 6-NCDF is a weak inducer of hepatic microsomal ethoxyresorufin O-deethylase activity and competitively binds to the aryl hydrocarbon (Ah) receptor but not the PR or ER. Thus both 6-NCDF and 2,3,7,8-TCDD, two ligands which bind to the Ah receptor, exhibit both partial estrogenic and antiestrogenic properties and serve as useful models for delineating the complex biochemical interactions between the ER and Ah receptor signal transduction pathways.

Animals↗

6-Methyl-1,3,8-trichlorodibenzofuran (MCDF) as an antiestrogen in human and rodent cancer cell lines: evidence for the role of the Ah receptor.

6-Methyl-1,3,8-trichlorodibenzofuran (MCDF) is a relatively nontoxic analog of 2,3,7,8-tetrachlorodibenzo-p-dioxin. Treatment of aryl hydrocarbon (Ah)-responsive MCF-7 human breast cancer cells with 100 nM MCDF resulted in the inhibition of 17 beta-estradiol-induced proliferation and the secretion of the 34-, 52-, and 160-kDa proteins. After treatment of the cells with 17 beta-[3H]estradiol, 100 nM of MCDF caused a decrease in the accumulation of the radiolabeled nuclear estrogen receptor (ER) complex in these cells. In parallel experiments, the antiestrogenic effects of MCDF were also determined in Ah-responsive wild-type Hepa 1c1c7 cells and Ah-nonresponsive class 1 and class 2 mutant cells. Treatment of the wild-type cells with 17 beta-[3H]estradiol and 100 nM MCDF caused a decrease in the accumulation of radiolabeled nuclear ER complex in these cells whereas no significant effects were observed in the mutant cells as determined by velocity sedimentation analysis. Comparable results were obtained using ER antibodies to measure the decrease in immunoreactive nuclear ER. In addition, both actinomycin D and cycloheximide inhibited the MCDF-mediated decrease of nuclear ER levels in the Hepa 1c1c7 wild-type cells. Although 100 nM MCDF did not induce cytochrome P-450-dependent monooxygenases in the MCF-7 or Hepa 1c1c7 cell lines, incubation of nuclear extracts from the MCF-7 cells treated with 100 nM MCDF with a synthetic consensus dioxin responsive element (an oligonucleotide duplex of 26 bases) gave a retarded band in a gel-retardation assay. The data suggest that the antiestrogenic effects of MCDF does not require the induction of the CYP1A1 gene expression but may involve the induction of other genes.

Animals↗

Inhibition of insulin-like growth factor-I responses in MCF-7 cells by 2,3,7,8-tetrachlorodibenzo-p-dioxin and related compounds.

Insulin-like growth factor-I (IGF-I) stimulated the growth and [3H]thymidine uptake in MCF-7 human breast cancer cells grown in serum- and growth factor-inactivated serum-containing media. Cotreatment of the cells with IGF-I plus 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) resulted in a significant decrease in mitogen-induced cell proliferation and [3H]thymidine uptake. Similar effects were observed for cells treated with 2,3,7,8-TCDD and IGF-I plus 17 beta-estradiol. The relative antimitogenic activities of 2,3,7,8-TCDD and related compounds followed the order 2,3,7,8-TCDD greater than 2,3,7,8-tetrachlorodibenzofuran (TCDF) greater than 1,2,7,8-TCDF greater than 1,3,7,8-TCDD which was similar to their aryl hydrocarbon (Ah) receptor binding affinities. The results showed that 2,3,7,8-TCDD did not alter the IGF-I receptor mRNA levels or the KD values for binding of [125I]IGF-I to the IGF-I receptor in MCF-7 cells. However, 2,3,7,8-TCDD significantly decreased the number of IGF-I-induced IGF-I receptor binding sites and this may play a role in the growth-inhibitory properties of 2,3,7,8-TCDD and related compounds and in the 'cross-talk' between the two endocrine-response pathways.

Benzofurans↗

Growth inhibitory and antimitogenic activity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in T47D human breast cancer cells.

The T47D human breast cancer cells used in this study express relative high levels of the progesterone receptor (637 +/- 118 fmol/mg protein) and lower levels of the estrogen and aryl hydrocarbon (Ah) receptors (81 +/- 3.4 and 55 +/- 8.2 fmol/mg protein, respectively). Treatment of these cells with 0.1, 1.0 and 10 nM concentrations of 17 beta-estradiol, transforming growth factor-alpha (TGF-alpha) and epidermal growth factor (EGF) resulted in concentration-dependent increase in cell proliferation and the ratios of mitogen-treated/control cell numbers were 2.46, 2.00 and 1.90, respectively. In contrast, insulin did not significantly stimulate T47D cell proliferation and insulin-like growth factor-I (IGF-I) was active only at a concentration of 10 nM. In parallel studies, the proliferative agents also stimulated the uptake of [3H]thymidine into cellular DNA. 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) did not affect T47D cell growth at concentrations of 0.1 and 1.0 nM, whereas at a concentration of 10 nM a 44% decrease in cell numbers was observed. In cells cotreated with TCDD plus 100 ng/ml insulin or 10 nM 17 beta-estradiol, EGF, TGF-alpha and IGF-I, TCDD caused a concentration-dependent decrease in cell proliferation and [3H]thymidine uptake. For example, at a 10 nM concentration of TCDD there was a 32, 45, 29, 25 and 32% decrease in the 17 beta-estradiol, TGF-alpha, EGF, IGF-I and insulin-induced cell growth, respectively. These results confirm the antiproliferative activity of TCDD in T47D cells and this was similar to results previously reported in MCF-7 human breast cancer cells for the interaction of TCDD and 17 beta-estradiol. In addition, the data also show that TCDD inhibits the growth stimulatory effects of other polypeptide growth factors in T47D cells.

Breast Neoplasms↗

Polynuclear aromatic hydrocarbon carcinogens as antiestrogens in MCF-7 human breast cancer cells: role of the Ah receptor.

Treatment of MCF-7 cells with 1.0 microM 3-methylcholanthrene (MC) caused a decrease in cell proliferation and [3H]thymidine uptake whereas no effects were observed at a lower (0.1 microM) concentration. Co-treatment of the cells with 1 nM 17 beta-estradiol plus 0.1 or 1.0 mu MC resulted in a significant inhibition of 17 beta-estradiol-induced growth and [3H]thymidine uptake. MC also inhibited the 17 beta-estradiol-induced secretion of the 52 kDa protein (procathepsin D) in MCF-7 cells and caused a concentration-dependent decrease in the nuclear estrogen receptor (ER) as determined by either velocity sedimentation analysis or immunoquantitation with human ER antibodies. The effects of several different polynuclear aromatic hydrocarbon (PAH) congeners on the nuclear ER in MCF-7 cells were also determined. Only those congeners which bound to the aryl hydrocarbon (Ah) receptor, namely benzo[a]pyrene, benz[a]anthracene, 7,12-dimethylbenz[a]anthracene and MC, caused a decrease in nuclear ER levels. In contrast, benzo[ghi]perylene, a congener which did not bind to the Ah receptor did not affect nuclear ER levels in MCF-7 cells. Moreover, with some congeners the decrease in nuclear ER levels could be observed without any significant induction of ethoxyresorufin O-deethylase activity, a P4501A1-dependent monooxygenase. These data suggest that the Ah receptor liganded with MC and related PAHs induced a broad spectrum of antiestrogenic responses in MCF-7 cells and complements the results of previous studies which report the antiestrogenic effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin and other halogenated aromatics which are also Ah receptor agonists.

Breast Neoplasms↗

DNA binding properties of the Ah receptor in wild-type and variant mouse hepatoma cells.

Mouse hepatoma Hepa 1c1c7 cells and nonresponsive mutants have been extensively used as models for investigating the molecular mechanism of induction of CYP1A1 gene transcription by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and related compounds. Incubation of cytosolic [3H]TCDD-aryl hydrocarbon (Ah) receptor from wild-type Hepa 1c1c7 cells for 16 h at 4 degrees C in 0.4 M KCl resulted in the formation of transformed liganded receptor which exhibited increased binding affinity on DNA-Sepharose columns. The elution properties of the peak with the highest DNA binding affinity were similar to the elution profiles of the nuclear receptor complex isolated from wild-type cells. TAOc1BPrcl (class I) nonresponsive mutant cells were characterized by relatively low levels of the cytosolic and nuclear Ah receptor complex. The BPrcl (class II) variant cell line contained levels of cytosolic receptor which were comparable to those observed in the wild-type cells; however, significantly reduced levels of nuclear receptor complex were observed in the class II variant cell line. Incubation of the nuclear or transformed liganded cytosolic Ah receptor from wild-type cells with a consensus 32P-labeled dioxin responsive element (DRE) in a gel shift assay gave a retarded band associated with the receptor-DRE complex. Incubation of the cytosolic receptor complex from the class I and II mutant cells for 16 h at 4 degrees C in 0.4 M KCl or for 2 h at 20 degrees C did not yield complexes with increasing binding affinities on DNA-Sepharose columns. Moreover, incubation of these complexes with 32P-labeled DRE did not give a retarded band in a gel shift assay. However, coincubation of the liganded class II mutant cytosol with cytosol from class I cells resulted in transformation of the liganded receptor and this was confirmed in both the DNA-Sepharose and gel retardation assays. These results suggest that the failure of class II mutant cells to respond to TCDD is due to a defect in the factors responsible for transformation of the cytosolic receptor complex.

Animals↗

Evidence for the mechanism of action of the 2,3,7,8-tetrachlorodibenzo-p-dioxin-mediated decrease of nuclear estrogen receptor levels in wild-type and mutant mouse Hepa 1c1c7 cells.

Treatment of wild-type Hepa 1c1c7 cells with 1 nM [3H]-17 beta-estradiol resulted in the rapid accumulation of the nuclear estrogen receptor complex whose levels were maximized within 1 hr. Cotreatment of the cells with 10 nM 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and [3H]-17 beta-estradiol did not affect the nuclear estrogen receptor levels 1 hr after addition of the radioligand; however, pretreatment of the cells for 1, 6, 24 or 42 hr with 10 nM TCDD prior to the addition of the radiolabeled hormone caused a greater than 50% decrease in nuclear estrogen receptor levels (determined by velocity sedimentation analysis) 1 hr after the addition of [3H]-17 beta-estradiol. In parallel experiments in which 10 nM TCDD was added 6 hr prior to the radiolabeled hormone, TCDD caused a 63 and 74% decrease in immunodetectable cytosolic and nuclear estrogen receptor protein levels, respectively, in the wild-type Hepa 1c1c7 cells. The nuclear estrogen receptor was also detected in two Hepa 1c1c7 mutant (class 1 and class 2) cell lines which have been characterized previously as TCDD non-responsive due to either decreased aryl hydrocarbon (Ah) receptor levels or a defect in the accumulation of transcriptionally active nuclear Ah receptor complexes, respectively. Treatment of these mutant cell lines with TCDD and [3H]-17 beta-estradiol (as described above) caused only a minimum (class 1) or non-detectable (class 2) decrease in nuclear estrogen receptor binding activity or immunodetectable protein levels. These results, coupled with the structure-dependent differences in the activities of TCDD (a strong Ah receptor agonist) and 2,8-dichlordibenzo-p-dioxin (a weak Ah receptor agonist) in this assay system, support a role for the Ah receptor in the TCDD-mediated decrease of the nuclear estrogen receptor in mouse Hepa 1c1c7 cells. In addition, actinomycin D and cycloheximide both inhibited the TCDD-mediated decrease of nuclear estrogen receptor levels in the Hepa 1c1c7 wild-type cells, and these results suggest that TCDD may induce specific gene products which are involved in this process.

Animals↗

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.

Affinity Labels↗

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.

Animals↗

6-Alkyl-1,3,8-trichlorodibenzofurans as antiestrogens in female Sprague-Dawley rats.

The comparative antiestrogenic effects of 6-methyl-1,3,8-trichlorodibenzofuran (MCDF), 6-t-butyl-1,3,8-trichlorodibenzofuran (triCDF) and 6-cyclohexyl-1,3,8-triCDF were determined in immature female Sprague-Dawley rats. Treatment of the animals with 17 beta-estradiol (0.33 mumol/kg X 2) caused an increase in uterine cytosolic and nuclear estrogen and progesterone receptor levels, uterine peroxidase activity, uterine wet weights and uterine epidermal growth factor (EGF) receptor binding activity and steady state EGF receptor mRNA levels. MCDF and 6-t-butyl-1,3,8-triCDF, two compounds which exhibit moderate aryl hydrocarbon (Ah) receptor binding affinity were also administered (100 mumol/kg) to the female rats in the presence or absence of 17 beta-estradiol. The results of these studies show that both compounds decrease the constitutive and 17 beta-estradiol-induced responses noted above. In contrast, 6-cyclohexyl-1,3,8-triCDF, a congener which exhibits low Ah receptor binding, was inactive as an antiestrogen. These studies clearly demonstrate that selected 6-alkyl-1,3,8-triCDFs elicit a broad spectrum of antiestrogenic activity in immature female rats. Moreover, in contrast to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) which also is a potent antiestrogen, the 6-alkyl-1,3,8-triCDFs are relatively non-toxic and can serve as prototypes for the future development of a new class of antiestrogens with potential for clinical applications.

Animals↗