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Methoxychlor induces proliferation of the mouse ovarian surface epithelium.

While the pesticide methoxychlor (MXC) has a variety of adverse effects on the female reproductive system, the effects of MXC on the ovarian surface epithelium (OSE) are unknown. Thus, this study tested the hypothesis that MXC alters the growth of the OSE. Mouse OSE cells were isolated by enzymatic digestion and cultured with vehicle, 3 microM of MXC, or 3 microM of 2,2-bis[p-hydroxyphenyl]-1,1,1,-trichloroethane (HPTE) for 14 days. After culture, proliferation and apoptosis were assessed by measurement of cell density, immunohistochemistry, and real-time polymerase chain reaction. Cell density was 66% greater for MXC-treated cells and 95% greater for HPTE-treated cells than controls (p < or = 0.05). The estrogen receptor blocker ICI 182,780 abolished MXC- and HPTE-induced increases in cell density. Proliferating cell nuclear antigen (PCNA) staining was positive in only 22 +/- 2.3% of controls, compared to 35 +/- 2.4% of MXC-treated cells and 40 +/- 2.4% of HPTE-treated cells (p < or = 0.05). The cell cycle regulators, cyclinD2 and cdk4, were significantly increased in MXC- and HPTE-treated cells compared to controls. The ApopTag assay demonstrated apoptotic cells in 4.8 +/- 0.45% of controls, 2.2 +/- 0.56% of MXC-treated cells, and 2.1 +/- 0.33% of HPTE-treated cells (p < or = 0.005). Expression of bcl-2 was significantly increased in MXC- and HPTE-treated cells, while bax was decreased in MXC- and HPTE-treated cells compared to controls. Collectively, these data indicate that MXC and HPTE stimulate OSE cell growth by increasing proliferation and inhibiting apoptosis. Further, since ICI 182,780 blocked MXC- and HPTE-induced OSE growth, these data suggest that the effects of MXC and HPTE on the OSE are mediated by estrogen receptors.

Animals↗

Methoxychlor directly affects ovarian antral follicle growth and atresia through Bcl-2- and Bax-mediated pathways.

Methoxychlor (MXC) is an organochlorine pesticide and reproductive toxicant. While in vivo studies indicate that MXC exposure increases antral follicle atresia, in part by altering apoptotic regulators (Bcl-2 and Bax), they do not distinguish whether MXC does so via direct or indirect mechanisms. Therefore, we utilized an in vitro follicle culture system to test the hypothesis that MXC is directly toxic to antral follicles, and that overexpression of anti-apoptotic Bcl-2, or deletion of pro-apoptotic Bax, protects antral follicles from MXC-induced toxicity. Antral follicles were isolated from wild-type (WT), Bcl-2 overexpressing (Bcl-2 OE), or Bax deficient (BaxKO) mice, and exposed to dimethylsulfoxide (control) or MXC (1-100 microg/ml) for 96 h. Follicle diameters were measured every 24 h to assess growth. After 96 h, follicles were histologically evaluated for atresia or collected for quantitative PCR analysis of Bcl-2 and Bax mRNA levels. MXC (10-100 microg/ml) significantly inhibited antral follicle growth at 72 and 96 h, and increased atresia (100 microg/ml) compared to controls at 96 h. Furthermore, MXC increased Bax mRNA levels between 48-96 h and decreased Bcl-2 mRNA levels at 96 h. While MXC inhibited growth of WT antral follicles beginning at 72 h, it did not inhibit growth of Bcl-2 OE or BaxKO follicles until 96 h. MXC also increased atresia of small and large WT and BaxKO antral follicles over controls, but it did not increase atresia of large Bcl-2 OE antral follicles over controls. These data suggest that MXC directly inhibits follicle growth partly by Bcl-2 and Bax pathways, and increases atresia partly through Bcl-2 pathways.

Animals↗

Methoxychlor inhibits brain mitochondrial respiration and increases hydrogen peroxide production and CREB phosphorylation.

The organochlorine insecticide methoxychlor (mxc) is an established reproductive toxicant that affects other systems including the central nervous system (CNS), possibly by mechanisms involving oxidative stress. This study tested the hypothesis that mxc inhibits brain mitochondrial respiration, resulting in increased production of reactive oxygen species (ROS). Oxygen electrode measurements of mitochondrial respiration and Amplex Red measurements of H(2)O(2) production were performed with rat brain mitochondria exposed in vitro to mxc (0-10 microg/ml) and with brain mitochondria from mice chronically exposed in vivo to mxc (0-64 mg/kg/day) for 20 days by intraperitoneal injection. In vitro mxc exposure inhibited ADP-dependent respiration (state 3) using both complex I- and II-supported substrates. Similarly, state 3 respiration was inhibited following in vivo mxc exposure using complex I substrates. H(2)O(2) production was stimulated after in vitro mxc treatment in the presence of complex I substrates, but not in mitochondria isolated from in vivo mxc-treated mice. Because previous studies demonstrated a relationship between oxidative stress and CREB phosphorylation, we also tested the hypothesis that mxc elevates phosphorylated CREB (pCREB) in mitochondria. Enzyme-linked immunosorbent assay (ELISA) measurements demonstrated that pCREB immunoreactivity was elevated by in vitro mxc exposure in the presence or absence of respiratory substrates, indicating that stimulation of H(2)O(2) production is not necessary for this effect. These multiple effects of mxc on mitochondria may play an important role in its toxicity, particularly in the CNS.

Animals↗

Effect of methoxychlor and estradiol on cytochrome p450 enzymes in the mouse ovarian surface epithelium.

Although the ovarian surface epithelium (OSE) is responsive to hormones and endocrine-disrupting chemicals, little information is available on the metabolizing capabilities of the OSE. Thus, we tested the hypothesis that the OSE is capable of expressing genes regulating phase I metabolism of estrogen and the estrogenic endocrine disruptor methoxychlor (MXC). To test this hypothesis, we isolated mouse OSE cells and cultured them with vehicle (dimethylsulfoxide; DMSO), 3 microM MXC, or 0.1 microM 17beta-estradiol (E2) +/- the anti-estrogen ICI 182,780 (1 microM) for 14 days. After culture, the cells were subjected to quantitative real-time polymerase chain reaction for cytochrome P450s (CYPs) 1A1, 1B1, 2C29, and 1A2, and estrogen receptor alpha (ERalpha). Our results indicate that E2 and MXC did not alter the expression of CYP1A1 or CYP1A2. In contrast, E2 significantly increased expression of CYP1B1 compared to controls (DMSO = 0.93 +/- 0.1, E2 = 3.12 +/- 0.64 genomic equivalents (GE), n = 4, p < or = 0.01). The E2-induced increase in CYP1B1 was abolished by co-treatment with ICI 182,780 (0.41 +/- 0.17 GE). MXC treatment did not affect CYP1B1 expression. Both MXC and E2 increased expression of CYP2C29 (DMSO = 0.02 +/- 0.003; MXC = 0.04 +/- 0.008; E2 = 0.46 +/- 0.03 GE, n = 4, p < or = 0.05). MXC- and E2-induced elevations in CYP2C29 were abolished by co-treatment with ICI 182,780 (0.02 +/- 0.005; 0.02 +/- 0.07 GE). In addition, E2 increased ERalpha expression 15-fold compared to controls (DMSO = 1.10 +/- 0.09, E2 = 15.0 +/- 3.60 GE, n = 3, p < or = 0.05), and ICI 182,780 abolished the E2-induced increase in ERalpha expression (1.85 +/- 1.09 GE). MXC treatment did not affect ERalpha expression. These data indicate that the OSE expresses enzymes known to metabolize native and xenoestrogens and that MXC and E2 modulate expression of some of them through ER-linked mechanisms.

Animals↗

Altered mammary gland development in male rats exposed to genistein and methoxychlor.

Genistein (GE) is a prevalent phytoestrogen whose presence in human and animal foods may affect biological actions of synthetic endocrine active compounds. We have previously reported that in utero and lactational exposure to high doses of GE or the endocrine active pesticide methoxychlor (MXC) caused mammary epithelial proliferation in 21-day-old male rats. Combined exposure to GE and MXC resulted in significant feminization of the male mammary glands. The goals of the current study were to evaluate mammary responses to GE and MXC at the adult stage and investigate relevant mechanisms. Following in utero, lactational exposure (through maternal diet), and direct dietary exposure, the inguinal mammary gland of male rats (90 days of age) was found to exhibit significant morphological alterations in the groups treated with GE and/or MXC compared to the control. GE exposure (at 300 and 800 ppm concentrations) caused lobular enlargement and epithelial proliferation, whereas MXC exposure (800 ppm) led to ductal elongation and lobular enlargement. Combining the two treatments caused prominent proliferation of both ducts and alveoli; secretory material was seen in readily recognizable alveolar lumens, which are absent in untreated male mammary. We also surveyed gene expression in the mammary tissue using a cDNA microarray and evaluated relevant protein factors. The results indicated that the treatment effects are likely due to interactions between steroid hormone receptor-mediated signals and growth factor-driven cellular pathways. The distinctive responses associated with the GE+MXC combination were likely linked to enhanced actions of insulin-like growth factor 1 and related downstream pathways.

Animals↗

Methoxychlor metabolites may cause ovarian toxicity through estrogen-regulated pathways.

The pesticide methoxychlor (MXC) is a reproductive toxicant that targets antral follicles of the mammalian ovary. Cytochrome P450 enzymes metabolize MXC to mono-OH MXC (1,1,1-trichloro-2-(4-hydroxyphenyl)-2-(4-methoxyphenyl)ethane [mono-OH]) and bis-OH MXC (1,1,1-trichloro-2,2-bis(4-hydroxyphenyl)ethane [HPTE]), two compounds that are proposed to be more toxic than the parent compound, can interact with the estrogen receptor (ER), and are proposed to be responsible for ovarian toxicity. Thus, this work tested the hypothesis that MXC metabolites may be responsible for inducing antral follicle-specific toxicities in the ovary and that this toxicity may be mediated through ER-regulated pathways. Mouse antral follicles were isolated and exposed to mono-OH (0.01-10 microg/ml), HPTE (0.01-10 microg/ml), or MXC (100 microg/ml) alone or in combination with ICI 182,780 (ICI; 1 microM) or 17beta-estradiol (E2; 10 and 50 nM) for 96 h. Follicle diameters were measured at 24-h intervals. After culture, follicles were morphologically evaluated for atresia. Both mono-OH and HPTE (10 microg/ml) inhibited follicle growth and increased follicle atresia. The antiestrogen, ICI, did not protect antral follicles from MXC or metabolite toxicity in regard to follicle growth or atresia, but E2 decreased MXC- and mono-OH-induced atresia in small antral follicles. These data suggest that MXC metabolites inhibit follicle growth and induce atresia and that ER-regulated pathways may mediate the ovarian toxicity of MXC and its metabolites.

Animals↗

Methoxychlor induces atresia of antral follicles in ERalpha-overexpressing mice.

Methoxychlor (MXC) is a pesticide that is known to bind to estrogen receptor alpha (ERalpha) and to induce atresia of antral ovarian follicles. Although studies have shown that MXC is toxic to the ovary, we hypothesize that perturbation to the estrogen-signaling system (i.e., increase or decrease in estrogen sensitivity) might alter ovarian responsiveness to MXC. Thus, we examined whether ERalpha overexpression alters the ability of MXC to increase follicle atresia. To do so, we employed a transgenic mouse model in which ERalpha can be inducibly overexpressed in animal tissues (ERalpha overexpressors). We dosed female controls and ERalpha overexpressors with sesame oil (vehicle control) or MXC (32 and 64 mg/kg/day) for 20 days. After dosing, the ovaries were collected for histological evaluation of follicle numbers and follicle atresia, while blood was collected for measurements of hormones. Estrous cycles were determined in all animals to ensure that all were terminated during estrus. Although there were no significant effects of MXC on the numbers of primordial, primary, and preantral follicles in both controls and ERalpha overexpressors, there was an effect on antral follicles. Specifically, our data indicate that 32 and 64 mg/kg MXC increased the percentage of atretic follicles compared to vehicle in both control and ERalpha overexpressor groups. Moreover, there was a clear trend toward greater sensitivity to 64 mg/kg MXC in ERalpha-overexpressing mice compared to control animals. Specifically, at the 64-mg/kg MXC dose, ERalpha-overexpressing mice had a significantly higher percentage of atretic follicles compared to control animals (controls = 21.5 +/- 3%, n = 5; ERalpha overexpressors = 37 +/- 23%, n = 9, p < or = 0.05 vs. controls). After 20 days of dosing, there were no differences in estradiol levels between controls and ERalpha-overexpressing mice in all treatment groups. Follicle-stimulating hormone (FSH) levels were similar in sesame oil-treated control mice and control mice treated with 32 mg/kg MXC, while control mice treated with 64 mg/kg MXC had significantly lower levels of FSH compared to sesame oil-treated controls (sesame oil = 4.31 +/- 0.7, MXC [64 mg/kg/day] = 1.89 +/- 0.4, n = 3, p < or = 0.02 vs. sesame oil). ERalpha-overexpressing mice treated with sesame oil, 32 or 64 mg/kg MXC, had similar FSH levels. Thus, we observed an increased percentage of atretic antral follicles in ERalpha-overexpressing mice treated with MXC compared to control mice treated with the same compound, suggesting that the ERalpha-signaling pathway plays an important role in MXC-induced atresia. The trend toward greater sensitivity to MXC in ERalpha-overexpressing mice compared to control animals cannot be explained by alterations in estradiol and/or FSH levels.

Animals↗

Methoxychlor inhibits growth and induces atresia of antral follicles through an oxidative stress pathway.

The mammalian ovary contains antral follicles, which are responsible for the synthesis and secretion of hormones that regulate estrous cyclicity and fertility. The organochlorine pesticide methoxychlor (MXC) causes atresia (follicle death via apoptosis) of antral follicles, but little is known about the mechanisms by which MXC does so. Oxidative stress is known to cause apoptosis in nonreproductive and reproductive tissues. Thus, we tested the hypothesis that MXC inhibits growth and induces atresia of antral follicles through an oxidative stress pathway. To test this hypothesis, antral follicles isolated from 39-day-old CD-1 mice were cultured with vehicle control (dimethylsulfoxide [DMSO]), MXC (1-100 microg/ml), or MXC + the antioxidant N-acetyl cysteine (NAC) (0.1-10 mM). During culture, growth was monitored daily. At the end of culture, follicles were processed for quantitative real-time polymerase chain reaction of Cu/Zn superoxide dismutase (SOD1), glutathione peroxidase (GPX), and catalase (CAT) mRNA expression or for histological evaluation of atresia. The results indicate that exposure to MXC (1-100 microg/ml) inhibited growth of follicles compared to DMSO controls and that NAC (1-10 mM) blocked the ability of MXC to inhibit growth. MXC induced follicular atresia, whereas NAC (1-10 mM) blocked the ability of MXC to induce atresia. In addition, MXC reduced the expression of SOD1, GPX, and CAT, whereas NAC reduced the effects of MXC on their expression. Collectively, these data indicate MXC causes slow growth and increased atresia by inducing oxidative stress.

Acetylcysteine↗

Methoxychlor-induced atresia in the mouse involves Bcl-2 family members, but not gonadotropins or estradiol.

Methoxychlor (MXC) is an organochlorine pesticide that increases the rate of ovarian atresia. To date, little is known about the mechanism by which MXC induces atresia. Because Bcl-2 (an antiapoptotic factor), Bax (a proapoptotic factor), gonadotropins, and estradiol are important regulators of atresia in the ovary, the purpose of this study was first to examine whether MXC-induced atresia occurred through alterations in Bcl-2 or Bax, and second, to examine the effect of MXC on gonadotropins, estradiol, and their receptors. CD-1 mice were dosed with 8-64 mg kg(-1) day(-1) MXC or vehicle (sesame oil). Ovaries were subjected to analysis of antral follicle numbers, Bcl-2, Bax, estrogen receptor, and follicle-stimulating hormone receptor levels. Blood was used to measure gonadotropins and estradiol. In some experiments, mice that overexpressed Bcl-2 or mice that were deficient in Bax were dosed with MXC or vehicle and their ovaries were analyzed for atresia. MXC caused a dose-dependent increase in the percentage of atretic antral follicles compared with controls at the 32 and 64 mg kg(-1) day(-1) doses of MXC. MXC treatment did not result in changes in Bcl-2 levels, but it did result in an increase in Bax levels in antral follicles. MXC treatment did not affect gonadotropin or estradiol levels, nor did it affect the levels of follicle-stimulating hormone or estrogen receptors. Mice that overexpressed Bcl-2 or mice that were deficient in Bax were protected from MXC-induced atresia. These data suggest that MXC induces atresia through direct effects on the Bax and Bcl-2 signaling pathways in the ovary.

Animals↗

Inhibitory effects of technical grade methoxychlor on development of neonatal male mouse reproductive organs.

Effects of technical grade methoxychlor (MX), an estrogenic insecticide, and 17 beta-estradiol (E2) were examined on serum testosterone (T) concentrations and growth and histology of neonatal male mouse reproductive organs. Male NIH/Swiss mice received i.p. injections daily from birth to Day 9 with one of the following: 10 micrograms E2 or 0.1 or 1.0 mg MX or sesame oil vehicle. The mice were killed on Day 10. MX or did not affect body weights or mortality. Serum T concentrations in control mice were 0.29 +/- 0.03 ng/ml; T concentrations in males treated with MX or E2 were reduced. The 1.0-mg dose of both MX and E2 significantly decreased DNA contents of the seminal vesicles (SV), bulbourethral glands (BUG), and ventral prostate (VP) compared to controls. In the same animals, DNA contents of testes, epididymides, and efferent ductules were not decreased. The lower dose of MX (0.1 mg) decreased DNA content of only BUG and SV. DNA content of the ductus deferens was not affected by any treatment. E2 and both doses of MX also decreased epithelial morphogenesis in the SV and BUG, and inhibited the onset of mucin production in BUG epithelium and smooth muscle differentiation in the ductus deferens. In summary, our results indicate that technical grade MX, at doses as low as 0.1 mg/day, and E2 inhibit neonatal male reproductive tract development and decrease serum T concentrations.

Animals↗

Enhancing effects of beta-estradiol 3-benzoate but not methoxychlor on the promotion/progression stage of chemically-induced mammary carcinogenesis in ovariectomized rats.

Modifying effects of beta-estradiol 3-benzoate (EB) and methoxychlor (MXC), a pesticide which possesses weak estrogenic activity, on 7,12-dimethylbenz(a)anthracene (DMBA)-induced mammary carcinogenesis were investigated in ovariectomized or intact female Sprague-Dawley rats. Twenty-eight weeks after a single DMBA (100 mg / kg body weight) initiation, when the incidence of mammary tumor-bearing rats had reached 75%, a number of the animals were subjected to ovariectomy in order to obtain 3 groups: i) tumor-bearing, ovariectomized group; ii) tumor-bearing, intact group; iii) no-tumor, ovariectomized group. Subsequently animals of each group were subjected to subcutaneous implantation of 0.5 mg EB or given diet containing 1000 ppm MXC for 13 weeks. Although the incidences, multiplicities and volumes of the palpable tumors gradually decreased after ovariectomy, EB treatment stimulated tumor growth in the tumor-bearing, ovariectomized group thereafter. A similar effect of EB treatment was also observed in the no-tumor, ovariectomized group. However, MXC did not show any effect in the tumor-bearing, or no-tumor ovariectomized groups, except that the multiplicity of tumors was significantly decreased by MXC treatment in the tumor-bearing, intact group. The results of our study suggest that MXC has no promotion / progression effect, but rather possesses a weak inhibitory effect, whereas the strongly estrogenic substance EB clearly enhanced DMBA-induced mammary tumorigenesis.

9,10-Dimethyl-1,2-benzanthracene↗

Uterotrophic action of the insecticide methoxychlor.

Dusting of rats and mice, as well as oral treatment with the insecticide methoxychlor, produced uterine weight increase in these rodents. Ablation of the ovaries, adrenals, or pituitary did not alter this effect, thus indicating a direct trophic action of this agent on the uterus. It is apparent that the application of this insecticide to animals used for hormonal experiments introduces an additional variable.

Animals↗

The biodegradation of methoxychlor by Klebsiella pneumoniae.

Klebsiella pneumoniae was found to effect the reductive dechlorination of methoxychlor (2,2-bis(p-methoxyphenyl)-1, 1, 1-trichloroethane) and its dihydroxy derivative (2, 2-bis (p-hydroxyphenyl)-1, 1, 1-trichloroethane) to dichloro derivatives 2, 2-bis (p-methoxyphenyl)-1, 1-dichloroethane and 2, 2-bis (p-hydroxyphenyl)-1, 1-dichloroethane, respectively. Dehydrohalogenation to the corresponding diaryl dichloroethylenes, which themselves were not further degraded by this bacterium, was not observed. Cleavage of the methoxy groups to form the hydroxy compounds did not take place.

Chemical Phenomena↗

Low-dose bioactivity of xenoestrogens in animals: fetal exposure to low doses of methoxychlor and other xenoestrogens increases adult prostate size in mice.

The hormonal activity of natural estrogens is influenced by the degree to which they bind to serum proteins. In the pregnant female and in the fetus, greater than 99% of estradiol may be bound by serum binding proteins. Therefore, even though total serum levels of estradiol appear very high in fetuses, we have found that in rodent fetuses, there is a very low free concentration of estradiol (0.2 pg/ml). Naturally occurring variation in fetal serum estradiol predicts differences in numerous postnatal traits, including prostate size. In addition, when this low level of free estradiol was experimentally increased from 0.2 to 0.3 pg/ml during the last third of fetal life, treated male mice showed an increase in adult prostate weight. Fetal exposure to low doses of xenobiotic estrogens by feeding to pregnant females, including the compounds methoxychlor (20 and 2000 micrograms/kg body weight), DES (0.02 to 2 micrograms/kg body weight) and bisphenol A (2 and 20 micrograms/kg body weight), also led to increased prostate weight in adulthood. In contrast, fetal doses of natural estradiol and DES above the physiological range of estrogenic activity, and within a toxicological dose range, led to the opposite outcome, a reduction in subsequent adult prostate weight. This indicates that it may be impossible to assess endocrine-disrupting activities in response to low doses within a physiological range of activity by using high, toxic doses of xenoestrogens in testing procedures. We have developed approaches in vitro to predict the potential estrogenic bioactivity of compounds in the physiologically relevant range in animals and humans. We address the following factors in predicting the final observed endocrine-disrupting effect in the animal: (1) the intrinsic estrogenic activity of a given molecule, (2) the effective free concentration determined by how the molecule is carried in serum, (3) partitioning between aqueous and lipid compartments in body and cell lipids, and (4) absorption and metabolism relative to the route of exposure. The studies and strategies we describe are important in developing criteria for a tiered testing system for the detection of estrogenic chemicals as well as endocrine-disrupting chemicals with different modes of action.

Animals↗

Methoxychlor disrupts uterine Hoxa10 gene expression.

Methoxychlor (MXC) is a pesticide that has adverse effects on reproductive capability in mice. MXC and its metabolites bind the estrogen receptor and function as endocrine disruptors. MXC diminishes the uterine decidual cell response, necessary for the support of pregnancy. Hoxa10 is an estrogen-regulated gene that is an essential mediator of the decidual response and necessary for pregnancy. Here we demonstrate that a mechanism by which MXC disrupts uterine function is by suppressing Hoxa10 expression. MXC treatment of mice produced a mild uterotropic response as measured by increased uterine weight and epithelial height. MXC treatment of uterine Ishikawa cells in vitro induced Hoxa10 expression. Estrogen receptor (ER) binding to the HOXA10 estrogen response element (ERE) was promoted by treatment with estradiol (E2); however, MXC disrupted E2/ER/ERE complex formation and gel shift. MXC alone allowed weak ER/ERE binding. In vivo MXC blocked the effect of E2 on Hoxa10 expression. Neonatal MXC treatment resulted in an immediate suppression and cellular restriction of Hoxa10 expression as well as a permanent generalized decrease in expression that persisted in the adult. MXC inhibited the expression of Hoxa10, a gene necessary for uterine development and function. One common mechanism by which endocrine disrupting chemicals produce lasting reproductive tract defects is through permanent alteration of developmental gene expression.

Animals↗

Developmental programming: differential effects of prenatal exposure to bisphenol-A or methoxychlor on reproductive function.

Increased occurrence of reproductive disorders has raised concerns regarding the impact of endocrine-disrupting chemicals on reproductive health, especially when such exposure occurs during fetal life. Prenatal testosterone (T) treatment leads to growth retardation, postnatal hypergonadotropism, compromised estradiol-positive feedback, polycystic ovaries, and infertility in the adult. Prenatal dihydrotestosterone treatment failed to affect ovarian morphology or estradiol-positive feedback, suggesting that effects of prenatal T may be facilitated via conversion of T to estradiol, thus raising concerns regarding fetal exposure to estrogenic endocrine-disrupting chemicals. This study tested whether fetal exposure to methoxychlor (MXC) or bisphenol A (BPA) would disrupt cyclicity in the ewe. Suffolk ewes were administered MXC (n=10), BPA (n=10) (5 mg/kg.d sc in cotton seed oil) or the vehicle (C; n=16) from d 30 to 90 of gestation. On d 60 of treatment, maternal MXC concentrations in fat tissue and BPA in blood averaged approximately 200 microg/g fat and 37.4+/-3.3 ng/ml, respectively. Birth weights of BPA offspring were lower (P<0.05) relative to C. There was no difference in the time of puberty between groups. BPA females were hypergonadotropic during early postnatal life and ended their breeding season later, compared with C. Characterization of cyclic changes after synchronization with prostaglandin F2alpha in five C, six MXC, and six BPA females found that the onset of the LH surge was delayed in MXC (P<0.05) and the LH surge magnitude severely dampened (P<0.05) in BPA sheep. These findings suggest that prenatal BPA and MXC exposure have long-term differential effects on a variety of reproductive endocrine parameters that could impact fertility.

Animals↗

Differential interaction of the methoxychlor metabolite 2,2-bis-(p-hydroxyphenyl)-1,1,1-trichloroethane with estrogen receptors alpha and beta.

Concern that some chemicals in our environment may affect human health by disrupting normal endocrine function has prompted research on interactions of environmental contaminants with steroid hormone receptors. We compared the activity of 2,2-bis-(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE), an estrogenic metabolite of the organochlorine pesticide methoxychlor, at estrogen receptor alpha (ERalpha) and estrogen receptor beta (ERbeta). Human hepatoma cells (HepG2) were transiently transfected with either human or rat ERalpha or ERbeta plus an estrogen-responsive, complement 3-luciferase construct containing a complement 3 gene promoter sequence linked to a luciferase reporter gene. After transfection, cells were treated with various concentrations of HPTE in the presence (for detecting antagonism) or absence (for detecting agonism) of 17beta-estradiol. HPTE was a potent ERalpha agonist in HepG2 cells, with EC50 values of approximately 5 x 10(-8) and 10(-8) M for human and rat ERalpha, respectively. In contrast, HPTE had minimal agonist activity with either human or rat ERbeta and almost completely abolished 17beta-estradiol-induced ERbeta-mediated activity. Moreover, HPTE behaved as an ERalpha agonist and an ERbeta antagonist with other estrogen-responsive promoters (ERE-MMTV and vtERE) in HepG2 and HeLa cells. This study demonstrates the complexity involved in determining the mechanism of action of endocrine-active chemicals that may act as agonists or antagonists through one or more hormone receptors.

Animals↗

Methoxychlor stimulates estrogen-responsive messenger ribonucleic acids in mouse uterus through a non-estrogen receptor (non-ER) alpha and non-ER beta mechanism.

This study examined the effects of the xenoestrogen methoxychlor (Mxc) on messenger RNA (mRNA) concentrations of two estrogen-responsive uterine genes, lactoferrin (LF) and glucose-6-phosphate dehydrogenase (G6PD). Ovariectomized wild-type (WT) and estrogen receptor (ER) alpha-knockout (ER alphaKO) mice were treated with Mxc or estradiol-17beta (E2) to determine whether Mxc acts via pathways that involve ER alpha. In WT mice, both E2 and Mxc stimulated increases in uterine LF and G6PD mRNA concentrations in a dose-dependent manner. Competitive pretreatment with the pure antiestrogen ICI 182,780 dramatically reduced E2-stimulated increases in mRNA concentrations but had no effect on Mxc-induced effects. Competitive pretreatment with E2 had only a partially inhibitory effect on Mxc-induced responses. In the ER alphaKO mouse, E2 had little effect on uterine LF or G6PD mRNA concentrations, whereas Mxc stimulated marked increases in both LF and G6PD mRNAs. The Mxc-induced increases in LF and G6PD mRNAs in the ER alphaKO mouse were not suppressed by competitive pretreatment with either E2 or ICI 182,780. Fold increases in mRNA concentrations for both genes induced by Mxc were similar for WT and ER alphaKO mice. The results surprisingly indicate that a xenoestrogen, Mxc, can increase LF and G6PD mRNA concentrations by a mechanism that is not mediated through ER alpha or ER beta, and acts through another pathway.

Animals↗