Depletion of follicles accelerated by combined exposure to phthalates and 4-vinylcyclohexene diepoxide, leading to premature ovarian failure in rats.

Humans are at daily risk by simultaneous exposures to a broad spectrum of man-made chemicals in the commercial products. Several classes of chemicals have been shown to alter follicle development and reduce fertility, leading to premature ovarian failure (POF) in mammals. We investigate the synergistic effects of 4-vinylcyclohexene diepoxide (VCD) and phthalate, including di(2-ethylhexyl) phthalate (DEHP), butyl benzyl phthalate (BBP) and di-n-butyl phthalate (DBP) on POF. Combination exposure with VCD and phthalate significantly reduced the numbers of primary follicles. The expressions of Amh and Sohlh2 were significantly decreased in the combination groups. Serum Amh levels were significantly lower in the combination groups. Additionally, serum levels of follicle-stimulating hormone were significantly increased in combination groups. Taken together, exposure to phthalates promotes the depletion of follicular follicles and consequently increases the risk of premature menopause, and combined exposure of phthalates and VCD to early menopausal women is likely to aggravate the POF syndrome.

Membrane-impermeable estrogen is involved in regulation of calbindin-D9k expression via non-genomic pathways in a rat pituitary cell line, GH3 cells.

Estrogen (E2) has been shown to regulate various functions for many pituitary hormones. Recently, the potential roles of non-genomic pathways in E2-induced actions have been proposed in the previous studies, however, the effects of E2 remain to be elucidated in regard to non-genomic induction of cytosolic protein calbindin-D9k (CaBP-9k). To gain a better understanding of the molecular events underlying E2-induced expression of CaBP-9k, rat pituitary tumor cells (GH3 cells) were treated with E-BSA (membrane impermeable E2-conjugated with BSA). Non-genomic induction of CaBP-9k by E-BSA was determined using RT-PCR and western blot analysis. The significant increase in CaBP-9k mRNA level was observed as early as 15 min following treatment with a high concentration of E-BSA (10(-6)M), whereas rapid and significant induction of CaBP-9k protein was noted at 5, 15 and 30 min after E-BSA exposure (p<0.05). In order to determine the potential involvement of different signaling pathways, several inhibitors were employed, i.e., ICI 182,780 for the estrogen receptor (ER) pathway, pertussis toxin (PTX) for the G-protein-coupled signaling pathway, U0126 (U) for the ERK (extracellular regulated kinase) and wortmannin (W) for the Akt (protein kinase B). Co-treatment with ICI 182, 780 and PTX reversed an E-BSA-induced increase in CaBP-9k mRNA and protein. Although neither U nor W alone attenuated E-BSA-induced effects, these inhibitors together abolished E-BSA-induced CaBP-9k expression, suggesting their involvement in its regulation. Taken together, these results demonstrate the involvement of various signaling pathways in E2-induced regulation of CaBP-9k. In addition, ER and G-protein-coupled signaling pathways may play central roles in the non-genomic activities of E2 and that downstream signaling via ERK and Akt are required to evoke ER-mediated induction of CaBP-9k in vitro.

Di-(2 ethylhexyl) phthalate and flutamide alter gene expression in the testis of immature male rats.

We previously demonstrated that the androgenic and anti-androgenic effects of endocrine disruptors (EDs) alter reproductive function and exert distinct effects on developing male reproductive organs. To further investigate these effects, we used an immature rat model to examine the effects of di-(2 ethylhexyl) phthalate (DEHP) and flutamide (Flu) on the male reproductive system. Immature male SD rats were treated daily with DEHP and Flu on postnatal days (PNDs) 21 to 35, in a dose-dependent manner. As results, the weights of the testes, prostate, and seminal vesicle and anogenital distances (AGD) decreased significantly in response to high doses of DEHP or Flu. Testosterone (T) levels significantly decreased in all DEHP- treated groups, whereas luteinizing hormone (LH) plasma levels were not altered by any of the two treatments at PND 36. However, treatment with DEHP or Flu induced histopathological changes in the testes, wherein degeneration and disorders of Leydig cells, germ cells and dilatation of tubular lumen were observed in a dose-dependent manner. Conversely, hyperplasia and denseness of Leydig, Sertoli and germ cells were observed in rats given with high doses of Flu. The results by cDNA microarray analysis indicated that 1,272 genes were up-regulated by more than two-fold, and 1,969 genes were down-regulated in response to DEHP, Flu or both EDs. These genes were selected based on their markedly increased or decreased expression levels. These genes have been also classified on the basis of gene ontology (e.g., steroid hormone biosynthetic process, regulation of transcription, signal transduction, metabolic process, biosynthetic process...). Significant decreases in gene expression were observed in steroidogenic genes (i.e., Star, Cyp11a1 and Hsd3b). In addition, the expression of a common set of target genes, including CaBP1, Vav2, Plcd1, Lhx1 and Isoc1, was altered following exposure to EDs, suggesting that they may be marker genes to screen for the anti-androgenic or androgenic effects of EDs. Overall, our results demonstrated that exposure to DEHP, Flu or both EDs resulted in a alteration of gene expression in the testes of immature male rats. Furthermore, the toxicological effects of these EDs on the male reproductive system resulted from their anti-androgenic effects. Taken together, these results provide a new insight into the molecular mechanisms underlying the detrimental impacts of EDs, in regards to anti-androgenic effects in humans and wildlife.

In vitro exposure to xenoestrogens induces growth hormone transcription and release via estrogen receptor-dependent pathways in rat pituitary GH3 cells.

In this study, we employed an in vitro model to examine the effects of endocrine disruptors (EDs) in the regulation of growth hormone (GH) gene, an important hormone in growth, development and body composition. The rat pituitary cells, GH3, were treated with alkyl-phenols (APs), i.e., 4-tert-octyl-phenol (OP), p-nonyl-phenol (NP) or bisphenol A (BPA) for 24h in a dose-dependent manner (10(-5), 10(-6) and 10(-7)M) and in a time-dependent fashion (1, 3, 6, 12 and 24h) at a high concentration (10(-5)M). An anti-estrogen, ICI 182,780, was used to examine the potential involvement of estrogen receptor (ER) in the induction of GH by EDs through an ER-mediated pathway. Treatment with OP, NP and BPA induced a significant increase in GH gene expression at high and medium doses at 24h. ED-exposure induced a marked increase in GH gene transcription as early as 6h and peaked at 12h. Co-treatment with ICI 182,780 significantly attenuated ED-induced GH expression in GH3 cells. Interestingly, the level of in vitro GH release was significantly increased at 24h in response to OP, NP or BPA, whereas co-treatment with ICI 182,780 significantly reversed ED-induced GH secretion, indicating that ER may take part in both GH gene transcription and its release in these cells. In addition, the activation of extracellular signal-regulated kinases (ERKs), protein kinases B (Akt) or G protein in response to OP, NP or BPA at 24h was observed in this study. Exposure to these APs resulted in a rapid and significant activation of ERK phosphorylation, reflecting that EDs-induced response may involve both genomic and non-genomic pathways in these cells. Taken together, these results may provide new insight into the mode of ED-induced action in GH gene regulation as well as the biological pathway underlying these molecular events.

Differential effects of flutamide and di-(2-ethylhexyl) phthalate on male reproductive organs in a rat model.

Endocrine disruptors (EDs) with androgenic and anti-androgenic effects may alter reproductive function by binding to androgenic receptors (AR) and inducing or modulating AR-dependent responses in the male reproductive system. However, the molecular mechanism(s) underlying these events remains unclear. In the present study, pregnant Sprague Dawley (SD) rats were treated with testosterone propionate (TP), flutamide (Flu) and di-(2-ethylhexyl) phthalate (DEHP) from gestation days (GD) 11 to 21. Interestingly, maternal exposure to Flu or DEHP caused fluctuations in the neonatal levels of serum testosterone (T) and luteinizing hormone (LH). Serum testosterone and LH were upregulated by Flu, but these hormones were down-regulated by DEHP. The anogenital distances (AGD) of male newborns were determined at post-neonatal days (PND) 1, 21 and 63. Male rats treated prenatally with DEHP (100 mg/kg mother's body weight) or Flu showed an AGD shorter than that of control rats. At PND 63, sperm concentration, viability and motility were reduced in the maternal DEHP and Flu-treated groups. The numbers of seminiferous tubules were reduced in the Flu and DEHP-treated offspring when compared with the vehicle- and TP-treated groups, and the tubules of the testes at PND 63 were disrupted by a high dose of Flu. In addition, we found differential gene expression patterns by microarray analysis following ED exposure, particularly in sex determination-related genes. Although Flu and DEHP are considered to be identical with regard to their anti-androgenic effects, their effects on developing male reproductive organs were distinct, suggesting that Flu competes with endogenous T, while DEHP influences a different step in androgenesis.

Estrogen receptors are involved in xenoestrogen induction of growth hormone in the rat pituitary gland.

Growth hormone (GH) plays a pivotal role in the regulation of growth, development and body composition. In order to provide new insights into estrogenic endocrine disruptor (ED) activities in the pituitary gland and the potential role played by estrogen receptors (ERs) in mediating their effects in vivo, we examined GH expression in the pituitary gland of an immature rat model. At postnatal day 14, immature rats were treated with various doses of 4-tert-octylphenol (OP), p-nonylphenol (NP) and bisphenol A (BPA), and the GH mRNA and protein expression levels were analyzed by real-time quantitative PCR and western blot/immunohistochemistry (IHC), respectively. An anti-estrogen (ICI 182780) was used to examine the potential involvement of ERs in ED-induced GH expression during critical windows of development. GH mRNA expression increased significantly 48 h after treatment with a high dose (600 mg/kg body weight [BW]) of OP or NP. However, this induction was abolished completely by co-treatment with ICI 182780. No significant difference in GH mRNA expression was observed following treatment with BPA or co-treatment of BPA with the anti-estrogen. Exposure to high doses (600 mg/kg BW) of these EDs significantly enhanced GH protein expression in the rat pituitary gland, whereas pretreatment with ICI 182780 markedly reduced this expression. Taken together, we have demonstrated for the first time that in vivo exposure to EDs can induce GH mRNA and protein expression in the rat pituitary gland and that their activities may involve an ER-mediated signaling pathway. These results may provide critical evidence for ED-induced dysregulation of pituitary GH expression and thus may be important for elucidating the potential impacts of EDs in altered body growth and development and for predicting the health risks of ED exposure in humans and wildlife.

Estrogen regulates the localization and expression of calbindin-D9k in the pituitary gland of immature male rats via the ERalpha-pathway.

Estrogen (E2; estradiol) plays a key role in the regulation of many pituitary hormones. It exerts its effects by binding to the intracellular estrogen receptor (ER), which then functions as a transcription factor. Although E2 has been shown to regulate calbindin-D(9k) (CaBP-9k) in the female reproductive system of rodents, the effects of E2 on the regulation of CaBP-9k in male rats remain to be elucidated. To investigate E2-induced regulation of the pituitary CaBP-9k gene, immature male rats were injected with E2 daily for 3 consecutive days with a dose of 40 microg/kg body weight (BW). The expression levels of CaBP-9k mRNA and protein were analyzed by RT-PCR and Western blot analysis, respectively, in the absence and presence of ICI 182,780 (ICI), an E2 antagonist. In addition, the tissue localization of CaBP-9k was determined by immunohistochemistry. CaBP-9k was localized in the cytoplasm of a specific cell type (acidophils) in the anterior lobe of the pituitary gland and highly expressed in the intermediate lobe. Exposure to E2 increased the number of cells that stained positive for CaBP-9k. To determine which ER subtype is involved in CaBP-9k regulation in the pituitary, the immature rats were treated with propyl pyrazole triol (PPT, an ERalpha-selective ligand) or diarylpropionitrile (DPN, an ERbeta-selective ligand) for 3 days. Pituitary CaBP-9k expression was mainly mediated by PPT in immature male rats, whereas no significant alteration of pituitary CaBP-9k gene expression was observed after DPN treatment. In addition, the estrogenicity of PPT in the induction of CaBP-9k expression was completely blocked by an estrogen antagonist, ICI, indicating that pituitary CaBP-9k expression is solely induced by ERalpha. Taken together, these results suggest that pituitary CaBP-9k is induced by E2 in male rats and its expression is predominantly regulated by ERalpha, but not ERbeta.

A calcium-binding protein, calbindin-D9k, is regulated through an estrogen-receptor mediated mechanism following xenoestrogen exposure in the GH3 cell line.

A variety of environmental chemicals may possess the potential to interact with various endocrine factors and consequently cause adverse effects on the reproductive, central nervous, and immune systems via the endocrine system(s). In this study, we used the GH3 cell line as an in vitro model to determine the effects of potential endocrine disruptors (EDs) on the induction of calbindin-D9k (CaBP-9k), a useful biomarker for detecting the estrogenic activities of EDs. A rat pituitary cell line, GH3, was treated with octyl-phenol (OP), nonyl-phenol (NP), and bisphenol A (BPA) in a dose-dependent manner (10(-5), 10(-6), and 10(-7)M) for 24 h. To determine the time dependency, the cells were exposed to a high concentration (10(-5)M) of OP, NP, and BPA and harvested at different time points (1, 3, 6, 12, and 24 h). An antiestrogen, ICI 182,780, was used to examine the potential involvement of the estrogen receptor (ER) in the induction of CaBP-9k by EDs via an ER-mediated pathway. Treatment with OP, NP, and BPA induced a significant increase in CaBP-9k expression at both the transcriptional and translational levels in a dose-dependent manner. Interestingly, ED exposure caused a significant increase in CaBP-9k messenger RNA (mRNA) expression at 6 h, whereas induction of CaBP-9k protein was observed as early as 1 h after treatment. However, both CaBP-9k mRNA and protein expression peaked at 24 h following treatment. The differential response of CaBP-9k mRNA and protein to EDs may be explained by translational efficiency. Cotreatment with ICI 182,780 significantly reversed ED-induced CaBP-9k expression in GH3 cells, suggesting that EDs may trigger the induction of CaBP-9k via an ER-mediated pathway in these cells. Taken together, these results demonstrate for the first time that a single in vitro exposure to OP, NP, or BPA results in an increase in CaBP-9k expression in GH3 cells, after 24 h. These results may contribute to our understanding of the relationship between the molecular events evoked by ED exposure and its biological effects on the pituitary gland in humans and animals. This in vitro model, in combination with a single injection in vivo method developed by us, may be important for elucidating additional details of the mode of action of xenoestrogens and may provide reliable tests for screening estrogenic agonists and antagonists.

Induction of uterine calbindin-D9k through an estrogen receptor-dependent pathway following single injection with xenobiotic agents in immature rats.

Various environmental chemicals, both natural and synthetic, are believed to act as endocrine disruptors (EDs) in mammals. In this study, a new in vivo model of immature rats was used to explore the induction of calbindin-D9k (CaBP-9k) following a single injection of EDs. In a time-dependent experiment, immature rats at postnatal day 16 were treated with high doses (600 mg/kg body weight [BW]) of 4-tert-octyphenol (OP), p-nonylphenol (NP), or bisphenol A (BPA), and euthanized at different time points (3, 6, 12, 24, or 48 h). For a dose-dependent study, immature rats were given different doses (200, 400, or 600 mg/kg BW) and euthanized at 24 h after injection. After treatment with these EDs, the effects on CaBP-9k mRNA and protein were examined by Northern and Western blot analyses, respectively. An anti-estrogen, ICI 182,780, was employed to examine the potential involvement of estrogen receptor (ER) in the induction of estrogen receptor-mediated physiologic responses in vivo. A single treatment with each of the chemicals, at 600 mg/kg BW, resulted in a significant increase in the expression of CaBP-9k mRNA and protein 24 h after injection. In addition, treatment with OP, NP, or BPA resulted in a positive uterotrophic response. Cotreatment with the ER antagonist ICI 182,780 completely prevented the ED-induced uterine weight gain. Taken together, these results demonstrate that a single injection of OP, NP, or BPA results in an increase of CaBP-9k mRNA and protein via an ER-dependent pathway in the uterus of immature rats. This new model may be important to elucidate the mechanism of action of xenoestrogens on estrogen-sensitive tissue.

Tetrabromodiphenyl ether (BDE 47) evokes estrogenicity and calbindin-D9k expression through an estrogen receptor-mediated pathway in the uterus of immature rats.

Polybrominated diphenyl ethers (PBDEs), a class of organic brominated flame retardants, have been increasing in the environment and in the tissues and milk of animals, including humans. To date, 209 PBDE congeners have been reported. Among these, 2,2',4,4'-tetrabromodiphenyl ether (BDE 47) is the dominant congener found in humans and animals. A number of studies have suggested that BDE 47 possesses the potential to disrupt the endocrine system, as well as reproductive functions. This suggests that BDE 47 may act as a developmental neurotoxin and endocrine disruptor. In this study, we employed immature rats as a developmental model to examine the potential involvement of BDE 47 in the induction of calbindin-D9k (CaBP-9k), which is a novel biomarker for screening estrogenic compounds. Beginning on postnatal day 16, BDE 47 was administered to immature rats in a dose- and time-dependent manner for 3 days. The biological effects of BDE 47 on the induction of CaBP-9k mRNA and protein were examined by semiquantitative RT-PCR and western blotting, respectively. In addition, the physiological role of the estrogen receptor (ER) in BDE 47-induced CaBP-9k expression was examined in vivo. Treatment with a high dose of BDE 47 (200 mg/kg body weight [BW]/day) resulted in a significant increase in CaBP-9k mRNA and protein 24 h after injection, whereas a modest increase was observed with low and medium doses (50 and 100 mg/kg BW/day). Additionally, treatment with the high dose of BDE 47 induced a clear uterotrophic response. Cotreatment with ICI 182,780, an ER antagonist, completely reversed the BDE 47-induced increases in uterine wet weight and CaBP-9k mRNA and protein. Taken together, these results demonstrate that BDE 47 exposure results in increases in CaBP-9k mRNA and protein in the uteri of immature rats. The biochemical pathway for BDE 47-induced activity may involve the ER-mediated signaling pathway. These results provide new insights into the estrogenic effects of BDE 47 at a critical developmental stage of the female reproductive system.

Analysis of gene expression profiles in the offspring of rats following maternal exposure to xenoestrogens.

Many environmental chemicals are known endocrine disruptors (EDs). These have the potential to alter endocrine systems via various mechanisms that include binding to hormone receptors, thereby either mimicking or blocking the hormone actions and causing abnormal gene expression. Here, to elucidate the molecular mechanism(s) underlying the detrimental effects associated with the estrogenicity of these chemicals, we determined whether gene profiles were altered in rats exposed to 4-tert-octyphenol (OP) and diethylstilbestrol (DES) in utero. Pregnant rats were treated with a high dose of OP (600 mg/kg BW per day) or DES (500 microg/kg BW per day) at gestational days (GD) 17, 18 and 19. Both dams and neonates were euthanized at lactation day (LD) 5. The transcript profiles of uterine tissue were compared in treated versus control in both maternal and neonatal sites using cDNA microarray to determine the expression levels of approximately 13,000 genes and expressed sequence tags (ESTs). The expression levels of some known estrogen-responsive genes, i.e., complement component 3, epidermal growth factor receptor or c-fos oncogene and calbindin 3, as well as some other randomly selected genes, including general transcription factor IIa, transcription factor 4 and lymphocyte specific 1, were increased by OP and/or DES treatment in the uteri of both maternal and neonate groups. However, the magnitude of these alterations in gene expression differed markedly between dams and neonates, most likely reflecting the temporal susceptibility of the reproductive tract to estrogenic chemicals. Importantly, the altered gene patterns identified by microarray analysis were confirmed by RT-PCR and real-time RT-PCR. Fifteen primers were designed to amplify specific altered genes. These genes were selected for validation because of their markedly increased expression levels and they were classified on the basis of gene ontology. Overall, a high correlation was observed between microarray and real-time PCR data. Taken together, these results indicate that placental exposure to OP or DES may cause temporal changes in gene expression in the uteri of dams and neonates. Moreover, these findings may provide useful indicators of the adverse effects of EDs and prove particularly important in elucidating the effects of xenoestrogens on estrogen-responsive tissues, such as the developing reproductive tract.