Biomedical subjects

L Biegel

Publications and source records attributed to L Biegel.

7 recordsLinked to original sources

PubMed1999

Screening methods for thyroid hormone disruptors.

The U.S. Congress has passed legislation requiring the EPA to implement screening tests for identifying endocrine-disrupting chemicals. A series of workshops was sponsored by the EPA, the Chemical Manufacturers Association, and the World Wildlife Fund; one workshop focused on screens for chemicals that alter thyroid hormone function and homeostasis. Participants at this meeting identified and examined methods to detect alterations in thyroid hormone synthesis, transport, and catabolism. In addition, some methods to detect chemicals that bind to the thyroid hormone receptors acting as either agonists or antagonists were also identified. Screening methods used in mammals as well as other vertebrate classes were examined. There was a general consensus that all known chemicals which interfere with thyroid hormone function and homeostasis act by either inhibiting synthesis, altering serum transport proteins, or by increasing catabolism of thyroid hormones. There are no direct data to support the assertion that certain environmental chemicals bind and activate the thyroid hormone receptors; further research is indicated. In light of this, screening methods should reflect known mechanisms of action. Most methods examined, albeit useful for mechanistic studies, were thought to be too specific and therefore would not be applicable for broad-based screening. Determination of serum thyroid hormone concentrations following chemical exposure in rodents was thought to be a reasonable initial screen. Concurrent histologic evaluation of the thyroid would strengthen this screen. Similar methods in teleosts may be useful as screens, but would require indicators of tissue production of thyroid hormones. The use of tadpole metamorphosis as a screen may also be useful; however, this method requires validation and standardization prior to use as a broad-based screen.

Animals↗

PubMed1992

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↗

PubMed1992

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↗

PubMed1991

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) and related compounds as antioestrogens: characterization and mechanism of action.

In the female Sprague-Dawley rat uterus 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and related compounds exhibited a broad spectrum of antioestrogenic responses. For example 2,3,7,8-TCDD inhibited the 17 beta-oestradiol-induced uterine wet weight increase, peroxidase activity, oestrogen and progesterone receptor levels, epidermal growth factor (EGF) receptor binding, and EGF receptor and c-fos protooncogene mRNA levels. The aryl hydrocarbon (Ah) receptor was identified in the rat uterus and the antioestrogenic activities of TCDD and related compounds were structure-dependent. In parallel studies, the effects of TCDD as an antioestrogen in MCF-7 human breast cancer cells was also investigated. TCDD inhibited the 17 beta-oestradiol-induced proliferation of these cells and the secretion of the 34-, 52- and 160-kDa proteins. Treatment of MCF-7 cells with 1 nM [3H]-17 beta-oestradiol resulted in a rapid accumulation of nuclear oestrogen receptor (ER) complexes. Pretreatment of the cells with TCDD caused a rapid decrease in nuclear ER binding activity and immunoreactive protein; moreover, the structure-dependent potencies of TCDD and related compounds as antioestrogens were similar to their Ah receptor binding affinities. TCDD also caused a decrease in nuclear ER levels in wild-type Ah-responsive Hepa 1c1c7 cells but was inactive in Ah non-responsive mutant Hepa 1c1c7 cells. Moreover, in the wild-type cells, both actinomycin D and cycloheximide blocked the effects of TCDD. 6-Methyl-1,3,8-trichlorodibenzofuran (MCDF) has previously been characterized as a TCDD antagonist in rodents and in transformed rodent cell lines. However, like TCDD, MCDF also exhibited a broad spectrum of antioestrogenic activities in both the female Sprague-Dawley rat uterus and MCF-7 cells. MCDF is relatively non-toxic compared to TCDD and is being investigated as a compound which may be clinically useful for the treatment of mammary cancer.

Animals↗

PubMed1990

Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on cell growth and the secretion of the estrogen-induced 34-, 52- and 160-kDa proteins in human breast cancer cells.

The effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on the growth of estrogen-responsive MCF-7 human breast cancer cells in the presence of 17 beta-estradiol was determined. After treatment with 17 beta-estradiol (1 nM), TCDD (10 nM) and 17 beta-estradiol (1 nM) plus TCDD (10 nM) the cells were monitored daily for cell growth and DNA content for 7 days. The results showed that TCDD inhibited cell proliferation and DNA content of untreated cells and inhibited the 17 beta-estradiol-stimulated cell proliferation and increase in cellular DNA content. In contrast, TCDD did not effect the growth of estrogen non-responsive MDA-MB-231 human breast cancer cells. TCDD (0.1-10 nM) also caused a concentration-dependent decrease in the 17 beta-estradiol-induced proliferation in MCF-7 cells. The effects of TCDD on the 17 beta-estradiol-induced secretion of the 52-kDa protein (i.e. procathepsin D), the 34-kDa (cathepsin D) and 160-kDa proteins were also determined in the MCF-7 and MDA-MB-231 human breast cancer cell lines. The levels of the proteins were determined by autoradiographic analysis of the incorporation of [35S]methionine into the secreted proteins which were separated by denaturing sodium dodecyl sulfate-polyacrylamide gel electrophoresis. Treatment of MCF-7 cells with 17 beta-estradiol (1 nM), TCDD (10 and 100 nM) and 17 beta-estradiol (1 nM) plus TCDD (10 nM) resulted in levels of the 52-kDa protein which were 497, 63.6, 98.1 and 66.3%, respectively, of the corresponding levels observed in control (untreated) cells. Using the same concentrations, the levels of the 34-kDa protein secreted into the media were 372, 42.3, 64.0 and 43.8% of control values, respectively, and the corresponding levels of the 160-kDa protein were 381, 52.9, 71.2 and 76.6% of the control values, respectively. In contrast, treatment of MDA-MB-231 cells with 17 beta-estradiol (1 nM), TCDD (10 and 100 nM) and 17 beta-estradiol (1 nM) plus TCDD (10 nM) resulted in a 31-39% reduction in the secretion of the 52-kDa protein however these effects were not statistically different from the control values. In addition, the treatments did not cause any significant effects on the secretion of the 34- and 160-kDa proteins by MDA-MB-231 cells. These results clearly confirm and extend the range of antiestrogenic effects caused by TCDD in estrogen-responsive MCF-7 cells and indicate that the MDA-MB-231 cells are not responsive to the antiestrogenic effects of TCDD.

Breast Neoplasms↗

PubMed1989

2,2',4,4',5,5'-hexachlorobiphenyl as a 2,3,7,8-tetrachlorodibenzo-p-dioxin antagonist in C57BL/6J mice.

At doses as high as 750 to 1000 mumol/kg, 2,2',4,4',5,5'-hexachlorobiphenyl (HCBP) did not cause fetal cleft palate, suppress the splenic plaque-forming cell response to sheep red blood cells, or induce hepatic microsomal ethoxyresorufin O-deethylase (EROD) in C57BL/6J mice. Despite the lack of activity of HCBP in eliciting any of these aryl hydrocarbon (Ah) receptor-mediated responses, competitive binding studies indicated that HCBP competitively displaced 2,3,7,8-[3H]tetrachlorodibenzo-p-dioxin (TCDD) from the murine hepatic cytosolic receptor. Cotreatment of C57BL/6J mice with TCDD (3.7 nmol/kg) and HCBP or 4,4'-diiodo-2,2',5,5'-tetrachlorobiphenyl (I2-TCBP) (400 or 1000 mumol/kg) showed that both compounds partially antagonized TCDD-mediated cleft palate and immunotoxicity (i.e., suppression of the splenic plaque-forming cell response to sheep red blood cells), and HCBP antagonized TCDD-mediated hepatic microsomal EROD induction. Thus, HCBP and I2-TCBP, like the commercial polychlorinated biphenyl mixture Aroclor 1254, were partial antagonists of TCDD action in C57BL/6J mice; however, it was also apparent from the results that Aroclor 1254 was the more effective antagonist at lower doses. Using [3H]TCDD, it was also shown that some of the effects of HCBP on TCDD-mediated cleft palate may be due to the decreased levels of TCDD found in the fetal palates after cotreatment with TCDD and HCBP. 4,4'-[125I2]diiodo-2,2',5,5'-tetrachlorobiphenyl ([125I2]TCBP) of high specific activity (3350 Ci/mmol) was synthesized and used to investigate the direct binding of this compound to the murine hepatic Ah receptor or other cytosolic proteins. No direct specific binding was observed between 125I2-TCBP and any cytosolic proteins using a sucrose density gradient assay procedure. These results contrasted with previous studies with Aroclor 1254 that suggested that this mixture acted as a competitive Ah receptor antagonist.

Animals↗

PubMed1989

6-Methyl-1,3,8-trichlorodibenzofuran (MCDF) as a 2,3,7,8-tetrachlorodibenzo-p-dioxin antagonist in C57BL/6 mice.

6-Methyl-1,3,8-trichlorodibenzofuran (MCDF), 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and TCDD plus MCDF were administered to C57BL/6 mice and their effects on several aryl hydrocarbon (Ah) receptor-mediated responses including hepatic microsomal aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) induction, immunotoxicity and teratogenicity were determined. MCDF did not induce hepatic microsomal AHH and EROD at doses up to 500 mumol/kg, however, co-administration of MCDF (50 mumol/kg) with a dose of TCDD which elicited a submaximal induction response (i.e. ED80-100, 15 nmol/kg) resulted in some small but significant inhibition of the induction of hepatic microsomal AHH and EROD (14 and 17%, respectively) compared to that observed with TCDD alone. Co-administration of TCDD and other doses of MCDF (10, 100, 200 or 500 mumol/kg) did not effect the induction response. These results were in contrast to the effectiveness of MCDF as an antagonist of the induction of AHH and EROD by TCDD in the rat (up to 50% inhibition of monooxygenase induction). Administration of MCDF (4, 20 and 40 mumol/kg) to C57BL/6 mice caused some inhibition of the splenic plaque-forming cell response to sheep erythrocytes only at the highest dose (26% decrease); the interaction of MCDF (4, 20 and 40 mumol/kg) and an immunotoxic dose of TCDD (3.7 nmol/kg) resulted in significant protection from the immunotoxic effects of TCDD at the 2 higher dose levels of MCDF. Similarly, MCDF (400 mumol/kg) did not cause cleft palate in mice but at this dose level MCDF afforded some protection from TCDD (20 micrograms/kg)-mediated cleft palate in mice. However, studies utilizing [3H]TCDD suggested that the protective effects may be due to modulation of TCDD reaching the palate in the co-treated animals (MCDF plus TCDD). Although both MCDF and Aroclor 1254 were both weak Ah receptor agonists in C57BL/6 mice, the former compound was much less effective as a TCDD antagonist. The observed species-specific effects for these 2 TCDD antagonists may be related species-dependent differences in receptor structure and receptor-ligand (i.e. agonist or antagonist) interactions.

Abnormalities, Drug-Induced↗