Xenoestrogens and breast cancer.
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Breast Neoplasms↗
Biomedical subjects
S H Safe
Publications and source records attributed to S H Safe.
Aryl hydrocarbon (Ah) nonresponsiveness in estrogen receptor-negative MDA-MB-231 cells is associated with expression of a variant arnt protein.
Several studies have reported a correlation between expression of the estrogen receptor (ER) and aryl hydrocarbon (Ah) responsiveness in human breast cancer cell lines. MDA-MB-231 cells are ER-negative and Ah-nonresponsive; however, initial studies showed that 2,3,7,8-tetrachlorodibenzo-p-dioxin induced CYP1A1 mRNA levels (5.8-fold) and chloramphenicol acetyltransferase activity (2.6-fold) in high passage (Hp, >50 passages) cells transiently transfected with an Ah-responsive plasmid. In contrast, no induction responses were observed in low passage (Lp, <20 passages) cells. The Ah responsiveness of Hp compared to Lp MDA-MB-231 cells was associated with a >2-fold increased expression of the Ah receptor in Hp cells. Further analysis revealed that the apparent molecular weight of the Ah receptor mRNA transcript and immunoreactive protein were comparable in Lp MDA-MB-231 and Ah-responsive human HepG2 cells. In contrast, RT-PCR analysis of the Ah receptor nuclear translocator (Arnt) protein showed that HepG2 cells expressed the expected 2.6-kb transcript, whereas a 1.3-kb transcript was the major product in MDA-MB-231 cells. Western blot analysis confirmed that HepG2 cells primarily expressed a 97-kDa wild-type form of Arnt, whereas a dominant 36-kDa variant was expressed in MDA-MB-231 cells. Complete sequence analysis of the variant form of Arnt revealed a major deletion of the C-terminal region of the protein (aa 330 to 789). Like HepG2 cells, the wild-type 2.6-kb transcript was detected in ER-positive (Ah-responsive) MCF-7 cells, whereas the low-molecular-weight variant Arnt was dominant in ER-negative MDA-MB-231, MDA-MB-435, and Adriamycin-resistant MCF-7 cells. These results suggest that expression of this protein may be useful as a prognostic factor in breast cancer.
Amino Acid Sequence↗
17 beta-Estradiol-mediated growth inhibition of MDA-MB-468 cells stably transfected with the estrogen receptor: cell cycle effects.
Estrogen receptor (ER)-negative MDA-MB-468 human breast cancer cells were stably transfected with wild-type human ER and utilized as a model for investigating estrogen- and aryl hydrocarbon (Ah)-responsiveness. Treatment of the stably transfected cells with 10 nM 17 beta-estradiol (E2) resulted in a significant inhibition (> 60%) of cell proliferation and DNA synthesis, which was blocked by 10(-7) M ICI 182 780. Analysis by flow cytometry indicated that treatment with E2 increased the percentage of cells in G0/G1 (from 68.8 to 89.4) and decreased cells in S (from 18.4 to 3.4) and G2/M (from 12.8 to 7.2) phases of the cell cycle. The effects of E2 on the major cyclins, cyclin-dependent kinases and cyclin-dependent kinase inhibitors, retinoblastoma protein (RB), E2F-1, and cyclin-dependent kinase activities were also investigated in the stably transfected MDA-MB-468 cells. The results demonstrated that the growth inhibitory effects of 10(-8) M E2 in ER stably transfected MDA-MB-468 cells were associated with modulation of several factors required for cell cycle progression and DNA synthesis, including significant induction of the cyclin-dependent kinase inhibitor p21cip-1 ( > 4-fold increase after 12 h) and decreased E2F1 and PCNA protein levels. These results show that the growth-inhibitory effects of E2 in the stably transfected cells were due to multiple factors which result in growth arrest in G0/G1 and inhibition of DNA synthesis.
Antineoplastic Agents↗
Inhibition of 3,3',4,4',5-pentachlorobiphenyl-induced chicken embryotoxicity by 2,2',4,4',5,5'-hexachlorobiphenyl.
3,3',4,4',5-Pentachlorobiphenyl (pentaCB) caused a dose-dependent induction of chicken embryolethality, malformations, edema, and liver lesions at doses ranging from 0.5 to 12.0 microg/kg. In contrast, no embryotoxicity was observed after treatment with 10, 25, or 50 mg/kg 2,2',4,4',5,5'-hexaCB. In eggs cotreated with 2.0 microg/kg, 3,3',4,4',5-pentaCB plus 10, 25, or 50 mg/kg 2,2',4,4',5,5'-hexaCB, there was significant protection from 3,3',4,4',5-pentaCB-induced embryo malformations, edema, and liver lesions, whereas no inhibition of embryolethality was observed. These results further extend the response-specific nonadditive interactions of binary mixtures of polychlorinated biphenyls (PCBs) and should be considered in the development of approaches for hazard assessment of PCB mixtures and related compounds.
Abnormalities, Drug-Induced↗
Characterization of the H4IIE rat hepatoma cell bioassay for evaluation of environmental samples containing polynuclear aromatic hydrocarbons (PAHs).
The H4IIE rat hepatoma cell bioassay has been extensively used to assess the toxic equivalents (TEQs) of complex mixtures of halogenated aromatic hydrocarbons in environmental samples. However, there is often a discrepancy between bioassay induction results and toxic equivalents calculated from chemical analysis of samples; the former generally yield higher bioassay-TEQs. Polynuclear aromatic hydrocarbons (PAHs) are a class of chemicals which can significantly contribute to induction-TEQs. Benzo(a)pyrene (BAP), dibenz(a, h)anthracene (DBA), benz(a)anthracene (BA), benzo(k)fluoranthene (BkF), benzo(b)fluoranthene (BbF), chrysene (Chr), and indeno(1,2,3-c,d) pyrene (IdP) are carcinogenic PAHs found in environmental samples, including oysters collected from Galveston Bay. The induction potency of these PAHs relative to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was determined individually in rat hepatoma H4IIE cells seeded in 6-well plates, and the induction-derived equivalency factors (EFs) relative to TCDD were 0. 000354, 0.00203, 0.000025, 0.00478, 0.00253, 0.00020, 0.0011 for BAP, DBA, BA, BkF, BbF, Chr, and IdP, respectively. Dilutions of a reconstituted PAH mixture containing 23 PAHs (744 to 4466 ng/g total PAHs) with constant percentages of BAP (4.5%), DBA (3.5%), BA (2.4%), BkF (3.7%), BbF (3.5%), Chr (4.7%), and IdP (4.2%) yielded bioassay-derived induction-EQs that ranged from 0.52 to 1.44 ng/g. Oysters exposed in the laboratory to the same PAH mixture for 30 days differentially accumulated the PAHs with time. Bioassay-EQs for these oyster extracts ranged from 0.94 to 5.79 ng/g. These results were similar to the chemically calculated EQs which varied from 0.81 to 3.13 ng/g.
Animals↗
Mechanism of inhibition of MDA-MB-468 breast cancer cell growth by 2,3,7,8-tetrachlorodibenzo-p-dioxin.
Treatment of estrogen receptor (ER)-negative MDA-MB-468 human breast cancer cells with 10 nM 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) induced formation of a nuclear aryl hydrocarbon (Ah) receptor complex as determined by ligand-binding and gel electrophoretic mobility shift assays. TCDD also induced CYP1A1-dependent activity in MDA-MB-468 cells, which represents the first ER-negative Ah receptor-positive human breast cancer cell line that has been identified. Treatment of this cell line with TCDD and related compounds also caused a 50% inhibition of cell growth, which resembled the growth inhibitory effects previously reported for epidermal growth factor (EGF). However, EGF expression is minimal in this cell line and is not induced by TCDD; moreover, EGF and TCDD induced a different pattern of oncogene expression and apoptosis in MDA-MB-468 cells. In contrast, TCDD caused a rapid and sustained induction of transforming growth factor alpha (TGF alpha) gene expression and secreted protein (nearly 2-fold); moreover, the growth-inhibitory effects of TCDD could be blocked by antibodies to the EGF receptor. In a separate experiment, it was shown that TGF alpha also inhibited growth of MDA-MB-468 cells. The results of this study indicate that the mechanism of growth inhibition of MDA-MB-468 cells by TCDD is due to induction of TGF alpha, which is a potent antimitogen in this cell breast cancer line.
Aryl Hydrocarbon Receptor Nuclear Translocator↗
Examination of the estrogenicity of 2,4,6,2',6'-pentachlorobiphenyl (PCB 104), its hydroxylated metabolite 2,4,6,2',6'-pentachloro-4-biphenylol (HO-PCB 104), and a further chlorinated derivative, 2,4,6,2',4',6'-hexachlorobiphenyl (PCB 155).
Several studies have reported that polychlorinated biphenyls (PCBs) exhibit estrogenic activity; however, it is not clear if these responses are associated with the polychlorinated hydrocarbon or its hydroxylated metabolite. In order to further test this hypothesis, a battery of in vitro and in vivo assays were used to investigate the estrogenic and antiestrogenic activities of 2,4,6,2',6'-pentachlorobiphenyl (PCB 104), its para-hydroxylated derivative 2,4,6,2',6'-pentachloro-4-biphenylol (HO-PCB 104), and its para-chlorinated derivative 2,4,6,2',4',6'-hexachlorobiphenyl (PCB 155). PCB 104 was found to 1) compete with tritiated 17beta-estradiol (E2) for binding to the mouse uterine estrogen receptor (ER); 2) induce gene expression in MCF-7 human breast cancer cells transiently transfected with the Gal4-human ER chimeric construct (Gal4-HEGO) and the Gal4-regulated luciferase reporter gene (17m5-G-Luc); and 3) increase MCF-7 cell proliferation in a dose-dependent manner. HO-PCB 104 exhibited greater estrogenic activity than PCB 104 in the in vitro assays examined. However, gas chromatographic-mass spectrophotometric analysis of extracts prepared from MCF-7 cells incubated with PCB 104 failed to detect the presence of the expected major metabolite HO-PCB 104. The estrogenic activity of the para-chlorinated derivative, PCB 155, was minimal compared to PCB 104 and HO-PCB 104, but it did exhibit significant antiestrogenic activity following co-treatment with 1 nM E2. Co-treatment of PCB 104 with 1 nM E2 had no effect on reporter gene expression compared to E2 alone, while 10 microM HO-PCB 104 exhibited additivity with 1 nM E2. At a dose of 202 mg/kg,PCB 104 increased uterine wet weight in ovariectomized CD-1 mice and induced vaginal epithelial cell cornification at 202, 16, and 1.7 mg/kg in a dose-dependent manner. These studies demonstrate that in addition to the hydroxylated metabolites, selected parent PCB congeners may also exhibit estrogenic and antiestrogenic activities.
Animals↗
Is there an association between exposure to environmental estrogens and breast cancer?
It was initially reported that levels of polychlorinated biphenyls (PCBs) or p,p'-DDE were elevated in breast cancer patients (serum or tissue) versus controls. These results, coupled with reports that selected environmental estrogens decreased 17beta-estradiol (E2) 2-hydroxylase activity and increased the ratio of 16alpha-hydroxyestrone/2-hydroxyestrone metabolites in MCF-7 human breast cancer cells, have led to the hypothesis that xenoestrogens are a preventable cause of breast cancer. More recent studies and analysis of organochlorine levels in breast cancer patients versus controls show that these contaminants are not elevated in the latter group. Moreover, occupational exposure to relatively high levels of PCBs and DDT/DDE are not associated with an increased incidence of breast cancer. A reexamination of the radiometric E2 2-hydroxylase assay in MCF-7 cells with diverse estrogens, antiestrogens, and carcinogens showed that the mammary carcinogen benzo[a]pyrene induced this response and the antiestrogen ICI 164,384 decreased E2 2-hydroxylase activity. Thus, E2 2-hydroxylase activity and the 16alpha-hydroxyestrone/2-hydroxyestrone metabolite ratio in MCF-7 cells does not predict xenoestrogens or mammary carcinogens.
Breast Neoplasms↗
Organochlorine exposure and risk for breast cancer.
Organochlorine industrial compounds, combustion products and pesticides have been widely identified in the environment and residues have been detected in extracts prepared from fish, wildlife, human tissues as well as human milk and serum. Many of these compounds possess sex steroid activities and therefore have the potential to disrupt endocrine-regulated homeostasis. Organochlorines which exhibit hormonal activity include: (i) polychlorinated biphenyls (PCBs), hydroxylated PCBs, o,p'-DDT, and other organochlorine insecticides which exhibit estrogen receptor (ER) agonist activities; (ii) p,p'-DDE, a ligand for the androgen receptor which exhibits antiandrogen activity; (iii) PCBs, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), and related aromatic hydrocarbons which bind the aryl hydrocarbon (Ah) receptor and exhibit tissue-specific antiestrogenic activity; and (iv) hydroxylated aromatics which bind transthyretin, a thyroid hormone binding protein. Although, it has been suggested that the estrogenic activity of PCBs and DDE may be a contributing factor for development of breast cancer in women, levels of these compounds are not consistently elevated in breast cancer patients and there is no evidence that women occupationally-exposed to relatively high levels of PCBs or DDE exhibit an increased incidence of breast cancer. In contrast, epidemiology studies suggest that women exposed to high levels of TCDD during an industrial accident in Seveso, Italy, have a decreased incidence of both breast and endometrial cancer. Based on the dietary intake of hormone or antihormone mimics derived from natural compounds in food, the estrogenic contribution of organochlorine compounds is small and their role in development of breast cancer is questionable.
Breast Neoplasms↗
Comparative 32P-postlabeling analysis of exogenous and endogenous DNA adducts in mouse skin exposed to a wood-preserving waste extract, a complex mixture of polycyclic and polychlorinated chemicals.
Wood preserving waste (WPW) sites contain numerous toxic compounds, including phenols, polycyclic aromatic hydrocarbons (PAHs), polychlorinated dibenzodioxins, and dibenzofurans. Previous in vitro and in vivo 32P-postlabeling studies showed the induction of multiple carcinogen-DNA adducts by WPW extracts. We now have tested the hypothesis in a mouse skin bioassay that a WPW extract not only causes the formation of exogenous, xenobiotic-derived DNA adducts, but also alters the levels of endogenous DNA modifications. Skin DNA of female ICR mice treated topically with an organic WPW extract was found by 32P-postlabeling to contain significantly increased levels of bulky oxidative DNA lesions (type II I-compounds), in addition to exogenous PAH-derived adducts. The mechanism of this increase is postulated to proceed through electrophilic quinoid compounds, which presumably were formed from phenols by chemical reactions of waste material or biologically by oxidative metabolism. On the other hand, the levels of another class of endogenous DNA adducts (type I I-compounds) were reduced significantly in exposed skin DNA. This effect was explained by the presence of cytochrome P450 inducers in the extract. All three types of DNA alterations observed may play a significant role in carcinogenesis. Our results imply that in addition to exogenous carcinogen-DNA adducts, alterations of endogenous DNA modifications may need to be considered in evaluating carcinogenic risk from toxic chemical wastes and the effects of remediation measures.
Acetone↗
Atypical cytochrome P450 induction profiles in glomerular mesangial cells at the mRNA and enzyme level. Evidence for CYP1A1 and CYP1B1 expression and their involvement in benzo[a]pyrene metabolism.
Recent studies in this laboratory have shown that benzo[a]pyrene (BaP) modulates growth factor-related gene expression and proliferation of renal glomerular mesangial cells (GMCs) in vitro. Because many of the toxic and biochemical effects of this polycyclic aromatic hydrocarbon are mediated through oxidative metabolism, the present studies were conducted to examine the patterns of cytochrome P450IA1 (CYP1A1) and P4501B1 (CYP1B1) inducibility in mesangial cells and the molecular consequences of this response. Exposure of cultured GMCs to BaP (30 microM) or 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD, 10 nM) for 24 hr induced CYP1A1 mRNA levels, a response abolished by cotreatment with 10 microM cycloheximide. The pattern of hydrocarbon inducibility was atypical in that BaP was a more effective inducer of CYP1A1 gene expression than TCDD, and both hydrocarbons induced aryl hydrocarbon hydroxylase (AHH) activity, but not ethoxyresorufin-O-deethylase activity. Cotreatment with alpha-naphthoflavone (alpha NF, 1 microM) or ellipticine (ELLIP, 0.1 nM) only partially inhibited the induction of AHH activity by BaP (30 microM). BaP and TCDD also induced expression of the CYP1B1 protein and the pattern of induction was comparable to that observed for CYP1A1. Treatment of GMCs with 30 microM BaP was associated with the formation of eight DNA adducts, and their occurrence could be inhibited by pretreatment with alpha NF (1 microM), but not ELLIP (0.1 nM). These results demonstrate that CYP1A1 and CYP1B1-related activities are induced in GMCs by BaP and TCDD and this induction is associated with metabolism of BaP to reactive intermediates that bind covalently to DNA.
Animals↗
Mutagenic potential of binary and complex mixtures using different enzyme induction systems.
A series of experiments was conducted to investigate the mutagenic potential of binary and complex mixtures in the presence and absence of inducible liver enzyme systems prepared with several different chemical inducers. Liver homogenate (S9, or 9000 x g supernatant) fractions were obtained from Sprague-Dawley rats induced with either Aroclor 1254 (AR), phenobarbital (PB), 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), or corn oil (UI). the mutagenic potential of test samples was measured with Salmonella typhimurium strain TA98 using each of the various S9 fractions. Test samples included benzo[a]pyrene (BaP), pentachlorophenol (PCP), a binary mixture of BaP and PCP, two five-component mixtures, a methylene chloride extract of wood preserving waste-amended soil, and a methanol extract of coal gasification waste. At a dose of 25 micrograms/plate, BaP produced 55, 83, 217, and 161 net revertants per plate with UI-, PB-, AR-, and TCDD-induced S9, respectively. The complex mixture extracted from the wood preserving waste-amended soil induced approximately equal responses with all four S9 mixes. At a dose of 250 micrograms/plate, the methanol extract of a coal gasification waste produced 56 net revertants using the uninduced S9; however, when Ar- and TCDD-induced S9 was used, 129 and 67 net revertants were observed, respectively. These data demonstrate the relative importance of the various induced cytochrome P-450 isozymes for the metabolism of mutagenic chemicals and complex mixtures.
Animals↗
Alteration of oxytocin-induced calcium oscillations in clone 9 cells by toxin exposure.
A communication-competent rat liver cell line (Clone 9) was examined as a model system to investigate the action of toxins on [Ca2+]i induced by extracellular signals. Clone 9 cells exhibit an initial [Ca2+]i spike followed by Ca2+ oscillations for at least 30 min after exposure to oxytocin (10 to 1000 nM). Oscillations of mitochondrial membrane potential were also detected using the potentiometric fluorescent probe rhodamine 123. Fast Fourier Transform showed that complex patterns of oscillations in Clone 9 cells exhibit both amplitude- and frequency-encoded signals. The initial Ca2+ peak and oscillations were not altered by ryanodine pretreatment but were suppressed by nifedipine and blocked by thapsigargin. Brief exposure of cells to the food-borne toxins patulin or gossypol or the environmental toxicant 2,3,7,8-tetrachlorodibenzo-p-dioxin at doses which have no effect on cell viability within the duration of experiments was used to monitor any changes in Ca2+ oscillations. Toxin treatment either blocked or changed the amplitude and/or frequency of Ca2+ oscillations depending upon the toxin-specific mechanisms of cellular injury. These studies indicate that toxic agents may alter amplitude- and frequency-encoded information derived from cell signaling events which could result in altered cellular homeostasis at nonlethal doses of toxin.
Animals↗
DNA damage induced in mouse tissues by organic wood preserving waste extracts as assayed by 32P-postlabeling.
Numerous wood preserving waste (WPW) sites in the United States pose genotoxic hazards. WPWs consist of complex mixtures containing toxic, including genotoxic, compounds which are derived from the preservatives coal tar creosote and pentachlorophenol (PCP) and other polychlorinated aromatics. The genotoxicity of WPW extracts, which has not been tested in mammals, cannot be evaluated on the basis of data for individual components because of possible compound interactions. Therefore, whole extracts need to be assayed. 32P-postlabeling represents a powerful tool to determine DNA adduct formation by complex genotoxic mixtures, such as cigarette smoke, diesel exhaust, and coke oven and foundry emissions in experimental animals and humans. In the present study, a mouse bioassay was used in combination with 32P-postlabeling to determine DNA adduct formation induced by hexane/acetone extracts of two samples from a WPW site. Female ICR mice were treated dermally with extract corresponding to 3 mg residue or vehicle control once per day for 2 days and killed 24 h later. Skin, lung, liver, kidney, and heart DNA preparations were assayed by nuclease P1-enhanced postlabeling. Adduct profiles were tissue-specific and displayed a multitude of non-polar DNA adducts with levels amounting to one adduct in 1.6 x 10(6) DNA nucleotides in skin (both extracts) and one adduct in 3.2 x 10(7) or 1.2 x 10(7) DNA nucleotides in liver (extract 1 or extract 2). Based on their chromatographic properties, these adducts appeared largely derived from polycyclic aromatic hydrocarbons (PAHs) present in the extracts. One of the major adducts was identified as the 32P-labeled derivative of the reaction product of 7 beta, 8 alpha-dihydroxy-9 alpha, 10 alpha-epoxy-7, 8,9,10-tetrahydrobenzo[a]pyrene (BPDE I) with N2 of deoxyguanosine. Total non-polar DNA adduct levels were highest in skin and lung, amounting to 17.4 and 24.0% of the skin values for extracts 1 and 2, respectively, in lung while the corresponding levels in liver were 5.0 and 12.6%. These results were in accord with the carcinogenic potencies of PAHs in these organs. Extract 2 induced higher adduct levels in internal organs, although its PAH concentrations were lower than those of extract 1, i.e. lung, liver, kidney, and heart had 1.4, 2.5, 1.9, and 1.7 times higher total adduct levels and 1.6, 3.3, 1.6, and 1.9 times higher benzo[a]pyrene adduct levels. With the exception of total adducts in lung, the differences between the two extracts were all significant, suggestive of compound interactions. The benzo[a]pyrene adduct levels in the five tissues correlated linearly with total adduct levels and thus represented a surrogate for the latter. Overall, the results suggest that DNA adducts in mouse tissues, as analyzed by 32P-postlabeling, are suitable biomarkers and dosimeters of the genotoxicity of WPW extracts.
Animals↗
Human chorionic gonadotropin protects Leydig cell function against 2,3,7,8-tetrachlorodibenzo-p-dioxin in adult rats: role of Leydig cell cytoplasmic volume.
2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) alters testicular steroidogenesis and reduces Leydig cell volume and number; however, human chorionic gonadotropin (hCG) stimulates testosterone production, increases the number and volume of Leydig cells and prevents TCDD's inhibition of testosterone production. The objective of this study was to determine if hCG protects Leydig cell function by maintaining sufficient Leydig cell cytoplasmic volume in TCDD-treated rats. Adult, male Sprague Dawley rats were divided into six treatment groups. Half of the animals received TCDD in corn oil (50 micrograms/kg body wt) and half received corn oil alone on Day 7 only. Additionally the rats received daily treatment of saline for 14 days, saline for 7 days and then hCG for 7 days, or hCG for 14 days. Rats were sacrificed on Day 14 and tissues collected. The decapsulated left testes were incubated in Eagles MEM for 2 h to determine basal production of testosterone and for 2 additional hours after the addition of hCG (100 IU) to the culture media. The right testis was evaluated by stereology to determine the volume of Leydig cells. Body weight was reduced (P < 0.01) in each TCDD-treated group; whereas, testicular weight was not affected by TCDD or hCG treatment. hCG prevented the TCDD-induced reduction in prostate and seminal vesicles weights. TCDD reduced the total volume of Leydig cell cytoplasm in saline-treated rats, but hCG eliminated the TCDD-induced reduction in Leydig cell cytoplasmic volume. hCG prevented the TCDD-induced reduction in Leydig cell function for both the 7- and 14-day treatments. Variation in the total volume of Leydig cell cytoplasm induced by the various treatment combinations was positively correlated with stimulated testosterone production in vitro (r = 0.486; P < 0.01) and the weight of the androgen sensitive organs (seminal vesicles, r = 0.562, P < 0.01; prostate, r = 0.380, P < 0.05). These data support the hypothesis that hCG prevents the TCDD-reduced Leydig cell function by maintaining sufficient Leydig cell cytoplasm and organelle content.
Animals↗
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.
Aldehyde Dehydrogenase↗
Environmental and dietary estrogens and human health: is there a problem?
It has been hypothesized that organochlorine pesticides and other environmental and dietary estrogens may be associated with the increased incidence of breast cancer in women and decreased sperm concentrations and reproductive problems in men. However, elevation of organochlorine compounds such as dichlorodipehenyldichloroethylene (DDE) and polychlorinated biphenyls (PCBs) in breast cancer patients is not consistently observed. Reanalysis of the data showing that male sperm counts decreased by over 40% during 1940 to 1990 indicated that inadequate statistical methods were used and that the data did not support a significant decline in sperm count. Humans are exposed to both natural and industrial chemicals which exhibit estrogenic and antiestrogenic activities. For example, bioflavonoids, which are widely distributed in foods, and several industrial compounds, including organochlorine pesticides and various phenolic chemicals, exhibit estrogenic activity. Humans are also exposed to chemicals which inhibit estrogen-induced responses such as the aryl hydrocarbon receptor (AhR) agonist 2,3,7,8-tetrachlorodibenzo-p-dioxin and related chlorinated aromatics, polynuclear aromatic hydrocarbon combustion products, and indole-3-carbinol, which is found in cruciferous vegetables. Many of the weak estrogenic compounds, including bioflavonoids, are also antiestrogenic at some concentrations. A mass balance of dietary levels of industrial and natural estrogens, coupled with their estimated estrogenic potencies, indicates that the dietary contribution of estrogenic industrial compounds is 0.0000025% of the daily intake of estrogenic flavonoids in the diet.(ABSTRACT TRUNCATED AT 250 WORDS)
Breast Neoplasms↗