Developmental effects of estrogenic agents on mice, fish, and frogs: a mini-review

Laboratory experiments have demonstrated that exposure of rodents to sex hormones during prenatal or early postnatal life can cause permanent and irreversible alterations of the endocrine and reproductive organs, such as ovary, fallopian tube, uterus, cervix, vagina, and mammary gland in females; and testis, epididymis, prostate, and seminal vesicle in males; as well as non reproductive organs including bones and muscle and immune and nervous systems in both sexes. Early development of Xenopus laevis into the tadpole and Fundulus heteroclitus goes through a rapid cell division, gastrulation, neurulation, and organogenesis within 1 week after fertilization. The developing embryo is very fragile and sensitive to estrogenic agents. Thus, these animals can be used as a suitable model for examining the effect of endocrine disruptors (hormonally active agents) on the development of aquatic living beings, which are most likely to be exposed to the compounds.     

Inflammatory repercussions in female steroid responsive glands after perinatal exposure to bisphenol A and 17-β estradiol

The mammary gland (MG) and female prostate are plastic reproductive organs which are highly responsive to hormones. Thus, endocrine disruptors, such as bisphenol A (BPA) and exogenous estrogens, negatively affect glandular homeostasis. In addition to previously described alterations, changes in inflammatory markers expression also trigger the development of a microenvironment that contributes to tumor progression. The current work aimed to evaluate the inflammatory responses of the MG and prostate gland to BPA (50 µg/kg) and 17-β estradiol (35 µg/kg) exposure during the perinatal window of susceptibility. The results showed that at 6 months of age there was an increase in the number of phospho-STAT3 (P-STAT3) positive cells in the female prostate from animals perinatally exposed to 50 µg/kg BPA daily. In addition, the number of macrophages increased in these animals in comparison with nonexposed animals, as shown by the F4/80 marker. Despite an increase in the incidence of lobuloalveolar and intraductal hyperplasia, the MG did not show any difference in the expression of the four inflammatory markers evaluated: tumor necrosis factor-α, COX-2, P-STAT3, and F4/80. Analysis of both glands from the same animal led to the conclusion that exposure to endocrine disruptors during the perinatal window of susceptibility leads to different inflammatory responses in different reproductive organs. As the prostate is more susceptible to these inflammatory mechanisms, it is reasonable to affirm that possible neoplastic alterations in this organ are related to changes in the inflammatory pattern of the stroma, a characteristic that is not evident in the MG.     

Developmental exposure to low-dose estrogenic endocrine disruptors alters sex differences in exploration and emotional responses in mice

Estrogenic endocrine disruptors (EEDs) are naturally occurring or man-made compounds present in the environment that are able to bind to estrogen receptors and interfere with normal cellular development in target organs and tissues. There is mounting evidence that EEDs can interfere with the processes of sexual differentiation of brain and behavior in different animal models. We investigated the effects of maternal exposure to EEDs, at concentrations within the range of human exposure and not patently teratogenic, on behavioral responses of male and female house mice (Mus musculus domesticus) before and after puberty. Pregnant dams were trained to spontaneously drink daily doses of corn oil with or without the estrogenic plastic derivative, bisphenol A (BPA 10 microg/kg), or the estrogenic insecticide methoxychlor (MXC 20 microg/kg) from gestation day 11 to postpartum day 8. Their male and female offspring were examined at different ages to examine several components of explorative and emotional behaviors in 3 experimental paradigms: a novelty test before puberty and, as adults, a free-exploratory open-field test and the elevated plus maze test. The main results are sex differences in control mice on a number of behavioral responses at both ages and in all experimental paradigms, while perinatal exposure to BPA or MXC decreased or eliminated such sex differences. The present findings are evidence of long-term consequences of developmental exposure to BPA and MXC on neurobehavioral development and suggest a differential effect of low-dose exposure to these estrogenic chemicals in males and females.     

Mammalian development in a changing environment: exposure to endocrine disruptors reveals the developmental plasticity of steroid-hormone target organs

Recent findings in the field of environmental endocrine disruption have revealed that developmental exposure to estrogenic chemicals induces morphological, functional, and behavioral anomalies associated with reproduction. The aim of the present study was to determine the effects of in utero exposure to low doses of the estrogenic chemical bisphenol A (BPA) on the development of the female reproductive tissues and mammary glands in CD-1 mice. Humans are exposed to BPA, which leaches from dental materials and plastic food and beverage containers. Here we report that prenatal exposure to BPA induces alterations in tissue organization within the ovaries and mammary glands and disrupts estrous cyclicity in adulthood. Because estrogen receptors are expressed developmentally in these estrogen-target organs, we propose that BPA may directly affect the expression of genes involved in their morphogenesis. In addition, alterations in the sexual differentiation of the brain, and thus the hypothalamic-pituitary-gonadal axis, may further contribute to the observed phenotype. The emerging field of endocrine disruptors promises to provide new insights into the mechanisms underlying the development of hormone-target organs and demonstrates that the environment plays important roles in the making of phenotypes.     

Early life exposure to endocrine-disrupting chemicals causes lifelong molecular reprogramming of the hypothalamus and premature reproductive aging

Gestational exposure to the estrogenic endocrine disruptor methoxychlor (MXC) disrupts the female reproductive system at the molecular, physiological, and behavioral levels in adulthood. The current study addressed whether perinatal exposure to endocrine disruptors re-programs expression of a suite of genes expressed in the hypothalamus that control reproductive function and related these molecular changes to premature reproductive aging. Fischer rats were exposed daily for 12 consecutive days to vehicle (dimethylsulfoxide), estradiol benzoate (EB) (1 mg/kg), and MXC (low dose, 20 μg/kg or high dose, 100 mg/kg), beginning on embryonic d 19 through postnatal d 7. The perinatally exposed females were aged to 16-17 months and monitored for reproductive senescence. After euthanasia, hypothalamic regions [preoptic area (POA) and medial basal hypothalamus] were dissected for real-time PCR of gene expression or pyrosequencing to assess DNA methylation of the Esr1 gene. Using a 48-gene PCR platform, two genes (Kiss1 and Esr1) were significantly different in the POA of endocrine-disrupting chemical-exposed rats compared with vehicle-exposed rats after Bonferroni correction. Fifteen POA genes were up-regulated by at least 50% in EB or high-dose MXC compared with vehicle. To understand the epigenetic basis of the increased Esr1 gene expression, we performed bisulfite conversion and pyrosequencing of the Esr1 promoter. EB-treated rats had significantly higher percentage of methylation at three CpG sites in the Esr1 promoter compared with control rats. Together with these molecular effects, perinatal MXC and EB altered estrous cyclicity and advanced reproductive senescence. Thus, early life exposure to endocrine disruptors has lifelong effects on neuroendocrine gene expression and DNA methylation, together with causing the advancement of reproductive senescence.     

Endocrine disruptors in bottled mineral water: estrogenic activity in the E-Screen

Human exposure to endocrine disruptors is well documented by biomonitoring data. However, this information is limited to few chemicals like bisphenol A or phthalate plasticizers. To account for so-far unidentified endocrine disruptors and potential mixture effects we employ bioassays to detect endocrine activity in foodstuff and consequently characterize the integrated exposure to endocrine active compounds. Recently, we reported a broad contamination of commercially available bottled water with estrogenic activity and presented evidence for the plastic packaging being a source of this contamination. In continuation of that work, we here compare different sample preparation methods to extract estrogen-like compounds from bottled water. These data demonstrate that inappropriate extraction methods and sample treatment may lead to false-negative results when testing water extracts in bioassays. Using an optimized sample preparation strategy, we furthermore present data on the estrogenic activity of bottled water from France, Germany, and Italy: eleven of the 18 analyzed water samples (61.1%) induced a significant estrogenic response in a bioassay employing a human carcinoma cell line (MCF7, E-Screen). The relative proliferative effects ranged from 19.8 to 50.2% corresponding to an estrogenic activity of 1.9-12.2 pg estradiol equivalents per liter bottled water. When comparing water of the same spring that is packed in glass or plastic bottles made of polyethylene terephthalate (PET), estrogenic activity is three times higher in water from plastic bottles. These data support the hypothesis that PET packaging materials are a source of estrogen-like compounds. Furthermore, the findings presented here conform to previous studies and indicate that the contamination of bottled water with endocrine disruptors is a transnational phenomenon.     

An updated review of environmental estrogen and androgen mimics and antagonists

For the last 40 y, substantial evidence has surfaced on the hormone-like effects of environmental chemicals such as pesticides and industrial chemicals in wildlife and humans. The endocrine and reproductive effects of these chemicals are believed to be due to their ability to: (1) mimic the effect of endogenous hormones, (2) antagonize the effect of endogenous hormones, (3) disrupt the synthesis and metabolism of endogenous hormones, and (4) disrupt the synthesis and metabolism of hormone receptors. The discovery of hormone-like activity of these chemicals occurred long after they were released into the environment. Aviation crop dusters handling DDT were found to have reduced sperm counts, and workers at a plant producing the insecticide kepone were reported to have lost their libido, became impotent and had low sperm counts. Subsequently, experiments conducted in lab animals demonstrated unambiguously the estrogenic activity of these pesticides. Man-made compounds used in the manufacture of plastics were accidentally found to be estrogenic because they fouled experiments conducted in laboratories studying natural estrogens. For example, polystyrene tubes released nonylphenol, and polycarbonate flasks released bisphenol-A. Alkylphenols are used in the synthesis of detergents (alkylphenol polyethoxylates) and as antioxidants. These detergents are not estrogenic; however, upon degradation during sewage treatment they may release estrogenic alkylphenols. The surfactant nonoxynol is used as intravaginal spermicide and condom lubricant. When administered to lab animals it is metabolized to free nonylphenol. Bisphenol-A was found to contaminate the contents of canned foods; these tin cans are lined with lacquers such as polycarbonate. Bisphenol-A is also used in dental sealants and composites. We found that this estrogen leaches from the treated teeth into saliva; up to 950 μg of bisphenol-A were retrieved from saliva collected during the first hour after polymerization. Other xenoestrogens recently identified among chemicals used in large volumes are the plastizicers benzylbutylphthalate, dibutylphthalate, the antioxidant butylhydroxyanisole, the rubber additive p-phenylphenol and the disinfectant o-phenylphenol. These compounds act cumulatively. In fact, feminized male fish were found near sewage outlets in several rivers in the U.K.; a mixture of chemicals including alkyl phenols resulting from degradation of detergents during sewage treatment seemed to be the causal agent. Estrogen mimics are just a class of endocrine disruptors. Recent studies identified antiandrogenic activity in environmental chemicals such as vinclozolin, a fungicide, and DDE, and insecticide. Moreover, a single chemical may produce neurotoxic, estrogenic and antiandrogenic effects. It has been hypothesized that endocrine disruptors may play a role in the decrease in the quantity and quality of human semen during the last 50 y, as well as in the increased incidence of testicular cancer and cryptorchidism in males and breast cancer incidence in both females and males in the industrialized word. To explore this hypothesis it is necessary to identify putative causal agents by the systematic screening of environmental chemicals and chemicals present in human foods to assess their ability to disrupt the endocrine system. In addition, it will be necessary to develop methods to measure cumulative exposure to (a) estrogen mimics, (b) antiandrogens, and (c) other disruptors.     

环境雌激素双酚A的研究进展

环境荷尔蒙是现代生命科学领域研究的热点之一,如今越来越多的人开始关注这一话题。在我们的生活环境中充斥着各种化学有毒试剂,其中,有一类物质能够模拟或抑制内分泌激素的活动,我们称之为内分泌干扰物。内分泌干扰物有能力改变内分泌系统的结构和功能。双酚A作为一种环境雌激素,属于内分泌干扰物的一种。双酚A被广泛应用于聚碳酸酯塑料和环氧树脂的制造。双酚A具有弱雌激素效应,能够与雌激素受体结合,引起内分泌系统的应答。目前的研究表明,双酚A会透过血胎屏障影响到胚胎发育,会对神经内分泌系统、肝组织功能以及生殖器的发育造成损伤。本文主要综述了环境雌激素双酚A在小鼠发育阶段所引起的诸多不利影响,并对环境荷尔蒙未来的研究方向进行了展望。     

Xenoestrogenic compounds promote capacitation and an acrosome reaction in porcine sperm

There is growing evidence that endocrine disruptors bind to hormone receptors; since these receptors are present on the sperm membrane, sperm are potentially a useful model for examining estrogenic activities of endocrine disruptors. The objective of the present study was to compare the effects of two xenoestrogenic compounds (genistein and 4-tert-octylphenol) to those of two steroids (estrogen and progesterone) and heparin on in vitro capacitation and the acrosome reaction in a porcine sperm model. Porcine sperm were incubated with various concentrations (0.001-100 μM) of each chemical for 15 or 30 min, and then capacitation and the acrosome reaction were assessed using chlortetracycline. Estrogen and progesterone were considerably more potent than the other chemicals in stimulating capacitation. Estrogen stimulated sperm capacitation at all tested concentrations after 15 min of incubation (P < 0.05), whereas progesterone stimulated sperm capacitation at all tested concentrations after 15 and 30 min (P < 0.05). The effect of genistein on sperm capacitation was comparable with that of estrogen, and it was the most potent in stimulating the acrosome reaction. Genistein stimulated the acrosome reaction at all tested concentrations after 30 min (P < 0.05). However, 4-tert-octylphenol had the least effect on capacitation and the acrosome reaction. In summary, since all chemicals studied effectively altered capacitation and the acrosome reaction, it was concluded that porcine sperm could be a useful model for in vitro screening of potential endocrine disruptors. It was noteworthy that concurrent comparisons to steroids increased the ability to determine estrogenic characteristics of the tested chemicals.     

Contribution of environmental pollutants to male infertily: a working model of germ cell apoptosis induced by plasticizers

Bisphenol A [2,2-bis(4-hydroxyphenyl)propane] (BPA), 4-nonylphenol (NP) and di(2-ethylhexyl)phthalate (DEHP), and its metabolite mono-2-ethylhexyl phthalate (MEHP) are chemicals found in plastics, which act as endocrine disruptors (EDs) in animals, including human. EDs act like hormones in the endocrine system, and disrupt the physiologic function of endogenous hormones. Most people are exposed to different endocrine disruptors and concern has been raised about their true effect on reproductive organs. In the testis, they seem to preferentially attack developing testis during puberty rather than adult organs. However, the lack of information about the molecular mechanism, and the apparently controversial effect observed in different models has hampered the understanding of their effects on mammalian spermatogenesis. In this review, we critically discuss the available information regarding the effect of BPA, NP and DEHP/ MEHP upon mammalian spermatogenesis, a major target of EDs. Germ cell sloughing, disruption of the blood-testis-barrier and germ cell apoptosis are the most common effects reported in the available literature. We propose a model at the molecular level to explain the effects at the cellular level, mainly focused on germ cell apoptosis.     

Establishment of a transgenic yeast screening system for estrogenicity and identification of the anti-estrogenic activity of malachite green

Endocrine disruptors refer to chemical compounds in the environment which interfere with the endocrine systems of organisms. Among them, environmental estrogens pose serious problems to aquatic organisms, in particular fish. It is therefore important and necessary to have a fast and low-cost system to screen the large number of different chemical compounds in the aquatic environment for their potential endocrine disrupting actions. In this study, a screening platform was developed to detect xenoestrogens in the aquatic environment using the fission yeast Schizosaccharomyces pombe, and applied for compound screening. The aim was to demonstrate any significant potential differences between the fish screening system and the human screening system. To this end, a yeast expression vector harboring a fish estrogen receptor alpha and a reporter vector containing the estrogen responsive element fused with the Escherichia coli LacZ gene were constructed. After transformation with these two vectors, the transformed yeast clones were confirmed by Western blotting and selected on the basis of the beta-galactosidase activity. In this transgenic yeast system, the natural estrogen (estradiol) and other known xenoestrogens such as diethylstilbestrol, bisphenol A, genistein and dichloro-diphenyl-trichloroethane exhibited dose-dependent activities. Using this system, more than 40 putative endocrine disruptors including phytoestrogens, pesticides, herbicides, industrial dyes and other industrial chemicals were screened. Ten of them were demonstrated to exhibit estrogenic actions. Industrial dyes such as malachite green (MG) that disrupt thyroid hormone synthesis are extensively used and are widely distributed in the aquatic environment. Using this system, MG did not show any estrogenic action, but was demonstrated to exhibit anti-estrogenic activity.     

A treatise on hazards of endocrine disruptors and tool to evaluate them

Hormones mediate a major part of our essential physiological functions. Both endogenous and exogenous compounds and their metabolites are known to act through hormone receptors leading to regulation of endocrine function. The endogenous ligands that control reproductive functions are generally steroids such as 17beta-estradiol, androgens, progesterone, pregnenolone and glucocorticoids. However, exogenous compounds that are structurally and functionally similar gain entry into animals including humans through the diet or by occupational exposures, causing endocrine disruption. In the recent decade, there is a lot of apprehension about the so-called "endocrine disruptors" which are wide spread in the environment, mainly due to unrestricted human activity. These compounds of anthropogenic or natural origin mimic the action of sex hormones and can interfere with the endocrine system. It has been hypothesized that environmental exposure to synthetic estrogenic chemicals and related endocrine active compounds may be responsible for malformations in the male reproductive tract, crytorchidism, hypospadias, decrease in sperm counts, decreased male reproductive capacity and even testicular cancers. The increasing concern in both public and scientific communities about these abnormalities have prompted the initiation of epidemiological studies to not only identify, but to also analyze the short and long term effects of endocrine disruptors. As a result, a number of assays have been developed and are undergoing validation aimed at high throughput screening of chemical agents that disrupt endocrine activity. This review consolidates the findings of epidemiological studies, particularly in relation to male reproductive disorders and brings to light the various types of in vitro and in vivo models that are available for tiered testing of suspected compounds.     

Sensitivity of expression of perivitelline membrane glycoprotein ZP1 mRNA in the liver of Japanese quail (Coturnix japonica) to estrogenic compounds

Avian perivitelline membrane protein, ZP1, is synthesized and secreted by the liver with the stimulation of estrogens. In the present study, we measured the expression of ZP1 gene in the liver of immature male quail treated with various estrogenic compounds and in the liver of male quail embryos that were developed in the fertilized eggs laid by mother quail injected with various estrogenic compounds during vitellogenesis. Total RNA extracted from the liver was reverse-transcribed and cDNA was subjected to real-time PCR. Both diethylstilbestrol and ethinyl estradiol caused significant effect on the increase in mRNA in immature male quail. In contrast, diethylstilbestrol administered via the route of maternal injection was not effective for induction of embryonic mRNA, although the effect of ethinyl estradiol administered via the same route was prominent. These results showed that direct administration of estrogenic compounds, diethylstilbestrol and ethinyl estradiol, stimulates the induction of ZP1 gene, but the rate of accumulation of these compounds in the yolk is different during vitellogenesis. The present studies suggest that although ZP1 gene is a sensitive biomarker to evaluate the effects of endocrine disruptors, the route of administration is an important factor to compare the effectiveness.     

Perturbateurs endocriniens et maladies métaboliques

During the last decades, there has been a dramatic increase in the prevalence of metabolic diseases, diabetes and obesity, which may be primarily related to changes in diet, lifestyle and behaviour. However, because of the parallel increase in pollution, in the use of chemicals for a variety of purposes, in drug consumption and because of additional evidence showing the involvement of the endocrine system in the regulation of metabolism and body weight, scientists have suspected the implication of endocrine disruptors in the developments of these conditions and diseases. Experimental studies have shown a possible role of diethyl stilbestrol, bisphenol A and dioxins/PCBs in endocrine disruption and obesity and highlighted the importance of exposure during vulnerable states such as the perinatal period. Some epidemiological studies also supported the possible role of these pollutants in metabolic diseases and obesity. Obesity is known to alter the kinetics of persistant organic chemicals such as dioxins and PCBs. These pollutants are stored in the adipose tissue, which may protect other more sensitive organs. However, during drastic weight loss, these pollutants are released in blood and tend to delay the improvement in metabolic parameters that are usually observed following weight loss. In conclusion, certain pollutants appear to play a role in the development of metabolic diseases and obesity, although their relative contribution as compared to other risk factor is unknown. In addition, obesity and weight loss alter the kinetics of certains pollutants and their toxicity.     

Motor hyperactivity caused by a deficit in dopaminergic neurons and the effects of endocrine disruptors: a study inspired by the physiological roles of PACAP in the brain

Recent studies have revealed that the pituitary adenylate cyclase-activating polypeptide (PACAP) might act as a psychostimulant. Here we investigated the mechanisms underlying motor hyperactivity in patients with pervasive developmental disorders, such as autism, and attention-deficit hyperactivity disorder (ADHD). We studied the effects of intracisternal administration of 6-hydroxydopamine (6-OHDA) or endocrine disruptors (EDs) on spontaneous motor activity (SMA) and multiple gene expression in neonatal rats. Treatment with 6-OHDA caused significant hyperactivity during the dark phase in rats aged 4-5 weeks. Motor hyperactivities also were observed after treatment with endocrine disruptors, such as bisphenol A, nonylphenol, diethylhexyl phthalate and dibutyl phthalate, during both dark and light phases. Gene-expression profiles produced using cDNA macroarrays of 8-week-old rats with 6-OHDA lesions revealed the altered expression of several classes of gene, including the N-methyl-D-aspartate (NMDA) receptor 1, glutamate/aspartate transporter, gamma-aminobutyric-acid transporter, dopamine transporter 1, D4 receptor, and peptidergic elements such as the galanin receptor, arginine vasopressin receptor, neuropeptide Y and tachykinin 2. The changes in gene expression caused by treatment with endocrine disruptors differed from those induced by 6-OHDA. These results suggest that the mechanisms underlying the induction of motor hyperactivity and/or compensatory changes in young adult rats might differ between 6-OHDA and endocrine disruptors.     

Antiestrogen therapies affect tissue homeostasis of the gerbil (Meriones unguiculatus) female prostate and ovaries

The present work aims to evaluate the response of the adult gerbil female prostate (paraurethral glands) and ovaries to short-term exposure to antiestrogenic agents, consisting of daily oral doses of letrozole (1 mg kg(-1) day(-1)) or intradermal doses of tamoxifen (1 mg/kg) every other day for 21 days. The serum levels of testosterone and estradiol were monitored, and the prostates and ovaries collected for structural, ultrastructural, and immunocytochemical analyses. The letrozole treatment resulted in increases of serum testosterone levels and secretory activity as well as in glandular hyperplasia and dysplastic growth, simulating the effects caused by the exogenous androgens. The effects caused by tamoxifen indicate that this endocrine agent acted as an estrogenic agonist on the prostate, causing glandular hypertrophy, secretory activity decrease, and the development of prostatic lesions. Therefore, it is possible to conclude that the letrozole and tamoxifen therapies result in a series of complex effects that endanger the physiology of hormone-dependent organs, including the female prostate and ovaries. The hormonal imbalance caused by administration of these drugs resulted in considerable changes in prostatic morphology, in a manner very similar to what occurs during the development of prostatic lesions in aged postmenopausal women. Thus, these therapies must be chosen carefully since long-term treatments can result in female prostate dysplasic lesions.     

Steroidogenic acute regulatory (StAR) protein and cholesterol side-chain cleavage (P450scc)-regulated steroidogenesis as an organ-specific molecular and cellular target for endocrine disrupting chemicals in fish

Biologically active steroids are synthesised de novo in specialised cells of several organs, including the adrenal gland, testis, ovary, brain, placenta and adipose tissue. Regardless of organ or tissue, the rate-limiting step in steroid hormone synthesis is the movement of cholesterol across the mitochondrial membrane (i.e. from the outer to the inner membrane) mediated by the steroidogenic acute regulatory (StAR) protein. Subsequent conversion of cholesterol to pregnenolone by cytochrome P450 side-chain cleavage (P450scc) represents the initiation of steroidogenesis. Chemically mediated disruption of StAR and P450scc expression may represent the first step in the sequence of related event cascades underlying xenoestrogen-induced toxicity and transmittable disturbances to the whole organism level. This may include, but is not limited to, alterations in sexual differentiation, growth, reproduction, development and metabolism. Despite the integral role of StAR and P450scc in acute steroidogenesis, and popular demand from regulatory agencies, bioassays for evaluating the effect of endocrine-disrupting chemicals have the potential to overlook chemicals that may modulate estrogenic responses through mechanisms that do not involve direct binding to estrogen receptors (ERs). In addition to their effect as direct ER agonists, the effects of endocrine disruptors may be evaluated and interpreted as interference with steroidogenesis and with the steroidal regulation of the normal development and function of juvenile, male and female individuals. Knowledge of these effects is scarce, indicating that relatively little is known about the mechanisms or mode-of-action of chemical alterations to steroidogenesis and their potential toxicity for wildlife species. In addition, analytical methods for the complete adaptation of these responses as biomarkers of response and effect are yet to be properly validated.     

Identification of estrogen-regulated genes by microarray analysis of the uterus of immature rats exposed to endocrine disrupting chemicals

Environmental estrogenic compounds which bind to the estrogen receptor (ER) can block or alter endogenous functions of estrogen in reproductive and developmental stages. A microarray technology is a very valuable method for the prediction of hormone-responsive activities in various gene expressions. Thus, we investigated the altered gene expression by estrogen and endocrine disruptors (EDs) using microarray technology in the uterus of immature rats. In this study, the expression levels of only 555 genes (7.42%) among the 7636 genes spotted on microarray chips were enhanced by more than two-fold following treatment with estradiol (E2), suggesting that direct or rapid response to E2 is widespread at the mRNA levels in these genes. In addition, elevated expression levels of the genes (over 2-fold) were observed by diethylstilbestrol (DES; 9.01%), octyl-phenol (OP; 8.81%), nonyl-phenol (NP; 9.51%), bisphenol-A (BPA; 8.26%) or genistein (9.97%) in the uterus of immature rats. The expression levels of representative genes, i.e., calbindin-D9k (CaBP-9k; vitamin D-dependent calcium-binding protein), oxytocin, adipocyte complement related protein (MW 30 kDa), lactate dehydrogenase A and calcium binding protein A6 (S100a6; calcyclin), were confirmed in these tissues by real-time PCR. In addition, the mRNA levels of these genes by real-time PCR were increased at follicular phase when E2 level was elevated during estrous cycle of adult female rats. In conclusion, these results indicate distinct altered expression of responsive genes following exposure to E2 and estrogenic compounds, and implicate distinct effects of endogenous E2 and environmental endocrine disrupting chemicals in the uterus of immature rats.