Pathway modeling of microarray data: a case study of pathway activity changes in the testis following in utero exposure to dibutyl phthalate (DBP).

Pathway activity level analysis, the approach pursued in this study, focuses on all genes that are known to be members of metabolic and signaling pathways as defined by the KEGG database. The pathway activity level analysis entails singular value decomposition (SVD) of the expression data of the genes constituting a given pathway. We explore an extension of the pathway activity methodology for application to time-course microarray data. We show that pathway analysis enhances our ability to detect biologically relevant changes in pathway activity using synthetic data. As a case study, we apply the pathway activity level formulation coupled with significance analysis to microarray data from two different rat testes exposed in utero to Dibutyl Phthalate (DBP). In utero DBP exposure in the rat results in developmental toxicity of a number of male reproductive organs, including the testes. One well-characterized mode of action for DBP and the male reproductive developmental effects is the repression of expression of genes involved in cholesterol transport, steroid biosynthesis and testosterone synthesis that lead to a decreased fetal testicular testosterone. Previous analyses of DBP testes microarray data focused on either individual gene expression changes or changes in the expression of specific genes that are hypothesized, or known, to be important in testicular development and testosterone synthesis. However, a pathway analysis may inform whether there are additional affected pathways that could inform additional modes of action linked to DBP developmental toxicity. We show that Pathway activity analysis may be considered for a more comprehensive analysis of microarray data.

Use of genomic data in risk assessment case study: II. Evaluation of the dibutyl phthalate toxicogenomic data set.

An evaluation of the toxicogenomic data set for dibutyl phthalate (DBP) and male reproductive developmental effects was performed as part of a larger case study to test an approach for incorporating genomic data in risk assessment. The DBP toxicogenomic data set is composed of nine in vivo studies from the published literature that exposed rats to DBP during gestation and evaluated gene expression changes in testes or Wolffian ducts of male fetuses. The exercise focused on qualitative evaluation, based on a lack of available dose-response data, of the DBP toxicogenomic data set to postulate modes and mechanisms of action for the male reproductive developmental outcomes, which occur in the lower dose range. A weight-of-evidence evaluation was performed on the eight DBP toxicogenomic studies of the rat testis at the gene and pathway levels. The results showed relatively strong evidence of DBP-induced downregulation of genes in the steroidogenesis pathway and lipid/sterol/cholesterol transport pathway as well as effects on immediate early gene/growth/differentiation, transcription, peroxisome proliferator-activated receptor signaling and apoptosis pathways in the testis. Since two established modes of action (MOAs), reduced fetal testicular testosterone production and Insl3 gene expression, explain some but not all of the testis effects observed in rats after in utero DBP exposure, other MOAs are likely to be operative. A reanalysis of one DBP microarray study identified additional pathways within cell signaling, metabolism, hormone, disease, and cell adhesion biological processes. These putative new pathways may be associated with DBP effects on the testes that are currently unexplained. This case study on DBP identified data gaps and research needs for the use of toxicogenomic data in risk assessment. Furthermore, this study demonstrated an approach for evaluating toxicogenomic data in human health risk assessment that could be applied to future chemicals.

Uncovering gene regulatory networks during mouse fetal germ cell development.

The commitment of germ cells to either oogenesis or spermatogenesis occurs during fetal gonad development: germ cells enter meiosis or mitotic arrest, depending on whether they reside within an ovary or a testis, respectively. Despite the critical importance of this step for sexual reproduction, gene networks underlying germ cell development have remained only partially understood. Taking advantage of the W(v) mouse model, in which gonads lack germ cells, we conducted a microarray study to identify genes expressed in fetal germ cells. In addition to distinguishing genes expressed by germ cells from those expressed by somatic cells within the developing gonads, we were able to highlight specific groups of genes expressed only in female or male germ cells. Our results provide an important resource for deciphering the molecular pathways driving proper germ cell development and sex determination and will improve our understanding of the etiology of human germ cell tumors that arise from dysregulation of germ cell differentiation.

Reproductive toxicity and pharmacokinetics of di-n-butyl phthalate (DBP) following dietary exposure of pregnant rats.

Most rodent developmental toxicity studies of dibutylphthalate (DBP) have relied on bolus gavage dosing. This study characterized the developmental toxicity of dietary DBP. Pregnant CD rats were given nominal doses of 0, 100, or 500 mg DBP/kg/day in diet (actual intake 0, 112, and 582 mg/kg/day) from gestational day (GD) 12 through the morning of GD 19. Rats were killed 4 or 24 hr thereafter. DBP dietary exposure resulted in significant dose-dependent reductions in testicular mRNA concentration of scavenger receptor class B, member 1; steroidogenic acute regulatory protein; cytochrome P450, family 11, subfamily a, polypeptide 1; and cytochrome P450 family 17, subfamily a, polypeptide 1. These effects were most pronounced 4 hr after the end of exposure. Testicular testosterone was reduced 24 hr post-exposure in both DBP dose groups and 4 hr after termination of the 500-mg DBP/kg/day exposure. Maternal exposure to 500 mg DBP/kg/day induced a significant reduction in male offspring's anogenital distance indicating in utero disruption of androgen function. Leydig cell aggregates, increased cord diameters, and multinucleated gonocytes were present in DBP-treated rats. Monobutyl phthalate, the developmentally toxic metabolite of DBP, and its glucuronide conjugate were found in maternal and fetal plasma, amniotic fluid, and maternal urine. Our results, when compared to previously conducted gavage studies, indicate that approximately equal doses of oral DBP exposure of pregnant rats, from diet or gavage, result in similar responses in male offspring.

GUDMAP: the genitourinary developmental molecular anatomy project.

In late 2004, an International Consortium of research groups were charged with the task of producing a high-quality molecular anatomy of the developing mammalian urogenital tract (UGT). Given the importance of these organ systems for human health and reproduction, the need for a systematic molecular and cellular description of their developmental programs was deemed a high priority. The information obtained through this initiative is anticipated to enable the highest level of basic and clinical research grounded on a 21st-century view of the developing anatomy. There are three components to the Genitourinary Developmental Molecular Anatomy Project GUDMAP; all of these are intended to provide resources that support research on the kidney and UGT. The first provides ontology of the cell types during UGT development and the molecular hallmarks of those cells as discerned by a variety of procedures, including in situ hybridization, transcriptional profiling, and immunostaining. The second generates novel mouse strains. In these strains, cell types of particular interest within an organ are labeled through the introduction of a specific marker into the context of a gene that exhibits appropriate cell type or structure-specific expression. In addition, the targeting construct enables genetic manipulation within the cell of interest in many of the strains. Finally, the information is annotated, collated, and promptly released at regular intervals, before publication, through a database that is accessed through a Web portal. Presented here is a brief overview of the Genitourinary Developmental Molecular Anatomy Project effort.

CCAAT/enhancer binding protein beta, but not steroidogenic factor-1, modulates the phthalate-induced dysregulation of rat fetal testicular steroidogenesis.

Prolonged in utero exposure of fetal male rats to dibutyl phthalate (DBP) can result in a feminized phenotype characterized by malformed epididymides, hypospadias, cryptorchidism, and retained thoracic nipples, among others. These symptoms likely result, in part, from decreased expression of steroidogenic enzymes and, therefore, reduced testosterone biosynthesis. However, the molecular mechanisms involved in these changes in gene expression profiles are unknown. To understand these mechanisms in rats, in vivo DNase footprinting was adapted to provide a semiquantitative map of changes in DNA-protein interactions in the promoter region of steroidogenic genes, including steroidogenic acute regulatory, scavenger receptor B-1, cytochrome P450 side chain cleavage, and cytochrome P450 17A1, that are down-regulated after an in utero DBP exposure. Regions with altered DNase protection were coordinated with a specific DNA binding protein event by EMSA, and binding activity confirmed with chromatin immunoprecipitation. Results demonstrated altered DNase protection at regions mapping to CCAAT/enhancer binding protein beta (c/ebp beta) and steroidogenic factor-1 (SF-1). Chromatin immunoprecipitation confirmed declines in DNA-protein interactions of c/ebp beta in DBP treated animals, whereas SF-1 was reduced in both diethyl phthalate (nontoxic) and DBP (toxic) treatments. These results suggest that inhibition of c/ebp beta, and not SF-1, is critical in DBP induced inhibition of steroidogenic genes. In addition, these observations suggest a pathway redundancy in the regulation of steroidogenesis in fetal testis. In conclusion, this study presents a snapshot of changes in the structure of transcriptional machinery and proposes a mechanism of action resulting from DBP exposure.

Fetal mouse phthalate exposure shows that Gonocyte multinucleation is not associated with decreased testicular testosterone.

The rat has been explored in detail for its in utero susceptibility to male reproductive tract malformation following phthalate exposure. Few other species have been studied in detail, and it is important for both mechanistic and risk assessment purposes to understand the species specificity of this response. We investigated the response of the fetal mouse testis to phthalate exposure and compared these results with those previously obtained from the rat. Initial experiments using a variety of phthalate congeners (monobutyl phthalate, di-(n-butyl) phthalate, or mono (2-ethylhexyl) phthalate) and exposure paradigms did not reduce fetal mouse testis testosterone levels. Pharmacokinetic data after a single 500 mg/kg di-(n-butyl)-phthalate (DBP) exposure on mouse gestation day (gd) 18 demonstrated that the concentrations and kinetics of the active metabolite monobutyl phthalate (MBP) in fetal and maternal plasma were similar to the rat. After a single 500 mg/kg or multiple day 250 mg/kg fetal mouse DBP exposure, rapid and dynamic changes in testis gene expression were observed, including induction of immediate early genes. Unlike the rat, expression of genes involved in cholesterol homeostasis and steroidogenesis were not decreased and were increased in a few cases. Similar to the rat, however, a 250- or 500-mg DBP/kg/day mouse exposure from gd 16 through 18 significantly increased seminiferous cord diameter, the number of multinucleated gonocytes per cord, and the number of nuclei per multinucleated gonocyte. Together, these results demonstrate that fetal mouse and rat phthalate exposure both induce immediate early gene expression and disrupt seminiferous cord and gonocyte development. This response in the mouse occurs without a measurable decrease in testicular testosterone, suggesting that altered seminiferous cord formation and gonocyte multinucleation may not be mechanistically linked to lowered testosterone.

Testicular gene expression profiling following prepubertal rat mono-(2-ethylhexyl) phthalate exposure suggests a common initial genetic response at fetal and prepubertal ages.

Phthalate chemical plasticizers can damage the fetal and postnatal mammalian testis, but several aspects of the injury mechanism remain unknown. Using a genome-wide microarray, the profile of testicular gene expression changes was examined following exposure of postnatal day 28 rats to a single, high dose (1000 mg/kg) of mono-(2-ethylhexyl) phthalate (MEHP). By microarray analysis, approximately 1675 nonredundant genes exhibited significant expression changes; the vast majority were observed at 12 h. Among the 36 genes significantly altered up to the 3-h time point, prominent functional categories were secreted, transcription, and signaling factors. Using quantitative PCR (qPCR), the dose-response of 24 genes was determined after a single MEHP exposure of 10, 100, or 1000 mg/kg. Increasing 114-fold by 12 h at 1000 mg/kg, Thbs1 (thrombospondin 1) showed the highest level of gene induction. The vast majority of genes analyzed by qPCR exhibited significant expression alterations at the lowest dose level. Interestingly, a unique, dose-dependent expression pattern was observed for the transcription factor Nr0b1, steroidogenic genes (Cyp17a1 and StAR), and a cholesterol metabolism gene (Dhcr7). For these genes, the direction of expression change at 10 or 100 mg/kg was opposite that observed at 1000 mg/kg. Gene profiling data at 1000 mg/kg MEHP were phenotypically anchored to increased germ cell apoptosis (6 and 12 h) and an interstitial neutrophil infiltrate (12 h). At 10 or 100 mg/kg MEHP, no testicular morphological changes were detected, but a significant increase in germ cell apoptosis was seen at 6 h. Finally, comparison of the prepubertal MEHP microarray data to similar data from fetal dibutyl phthalate (DBP) exposure showed conservation in both the identities of testicular genes altered and the direction of expression changes. For example, 60% of the genes altered within 3 h of prepubertal MEHP exposure also were changed following acute fetal DBP exposure, and the direction of expression change was highly preserved. These data demonstrate that similar genetic targets are altered following fetal and prepubertal phthalate exposure, suggesting that the initial mechanism of fetal and prepubertal phthalate-induced testicular injury is shared.

Altered gene expression during rat Wolffian duct development following di(n-butyl) phthalate exposure.

Di(n-butyl) phthalate (DBP) is a common plasticizer and solvent that disrupts androgen-dependent male reproductive development in rats. In utero exposure to 500 mg/kg/day DBP on gestation days (GD) 12 to 21 decreases androgen biosynthetic enzymes, resulting in decreased fetal testicular testosterone levels. One consequence of prenatal DBP exposure is malformed epididymides in adult rats. Reduced fetal testosterone levels may be responsible for the malformation, since testosterone is required for Wolffian duct stabilization and their development into epididymides. Currently, little is understood about the molecular mechanisms of Wolffian duct differentiation. The objective of this study was to identify changes in gene expression associated with altered morphology of the proximal Wolffian duct following in utero exposure to DBP. Pregnant Crl:CD(R) (SD) rats were gavaged with corn oil vehicle or 500 mg/kg/day DBP from GD 12 to GD 19 or 21. There were only small morphological differences between control and DBP-exposed Wolffian ducts on GD 19. On GD 21, 89% of male fetuses in the DBP dose group showed marked underdevelopment of Wolffian ducts, characterized by decreased coiling. RNA was isolated from Wolffian ducts on GD 19 and 21. Together with empirical information, cDNA microarrays were used to help identify candidate genes that could be associated with the morphological changes observed on GD 21. These candidate genes were analyzed by real-time RT-PCR. Changes in mRNA expression were observed in genes within the insulin-like growth factor (IGF) pathway, the matrix metalloproteinase (MMP) family, the extracellular matrix, and in other developmentally conserved signaling pathways. On GD 19, immunolocalization of IGF-1 receptor protein demonstrated an increase in cytoplasmic expression in the mesenchymal and epithelial cells. There was also a variable decrease in androgen receptor protein in ductal epithelial cells on GD 19. This study provides insight into the effects of antiandrogens on the molecular mechanisms involved in Wolffian duct development. The altered morphology and changes in gene expression following DBP exposure are suggestive of altered paracrine interactions between ductal epithelial cells and the surrounding mesenchyme during Wolffian duct differentiation due to lowered testosterone production.

Di-n-butyl phthalate activates constitutive androstane receptor and pregnane X receptor and enhances the expression of steroid-metabolizing enzymes in the liver of rat fetuses.

The plasticizer di-n-butyl phthalate (DBP) is a reproductive toxicant in rodents. Exposure to DBP in utero at high doses alters early reproductive development in male rats. Di-n-butyl phthalate also affects hepatic and extrahepatic enzymes. The objectives of this study were to determine the responsiveness of steroid-metabolizing enzymes in fetal liver to DBP and to investigate the potential of DBP to activate nuclear receptors that regulate the expression of liver enzymes. Pregnant Sprague-Dawley rats were orally dosed with DBP at levels of 10, 50, or 500 mg/kg/day from gestation days 12 to 19; maternal and fetal liver samples were collected on day 19 for analyses. Increased protein and mRNA levels of CYP 2B1, CYP 3A1, and CYP 4A1 were found in both maternal and fetal liver in the 500-mg dose group. Di-n-butyl phthalate at high doses also caused an increase in the mRNA of hepatic estrogen sulfotransferase and UDP-glucuronosyltransferase 2B1 in the dams but not in the fetuses. Xenobiotic induction of CYP3A1 and 2B1 is known to be mediated by the nuclear hormone receptors pregnane X receptor (PXR) and constitutive androstane receptor (CAR). In vitro transcriptional activation assays showed that DBP activates both PXR and CAR. The main DBP metabolite, mono-butyl-phthalate (MBP) did not interact strongly with either CAR or PXR. These data indicate that hepatic steroid- and xenobiotic-metabolizing enzymes are susceptible to DBP induction at the fetal stage; such effects on enzyme expression are likely mediated by xenobiotic-responsive transcriptional factors, including CAR and PXR. Our study shows that DBP is broadly reactive with multiple pathways involved in maintaining steroid and lipid homeostasis.

Analysis of variation of amplitudes in cell cycle gene expression.

BACKGROUND: Variation in gene expression among cells in a population is often considered as noise produced from gene transcription and post-transcription processes and experimental artifacts. Most studies on noise in gene expression have emphasized a few well-characterized genes and proteins. We investigated whether different cell-arresting methods have impacts on the maximum expression levels (amplitudes) of a cell cycle related gene. RESULTS: By introducing random noise, modeled by a von Mises distribution, to the phase angle in a sinusoidal model in a cell population, we derived a relationship between amplitude and the distribution of noise in maximum transcription time (phase). We applied our analysis to Whitfield's HeLa cell cycle data. Our analysis suggests that among 47 cell cycle related genes common to the 2nd experiment (thymidine-thymidine method) and the 4th experiment (thymidine-nocodazole method): (i) the amplitudes of CDC6 and PCNA, which are expressed during G1/S phase, are smaller in the 2nd experiment than in the 4th, while the amplitude of CDC20, which is expressed during G2/M phase, is smaller in the 4th experiment; and (ii) the two cell-arresting methods had little impact on the amplitudes of the other 43 genes in the 2nd and 4th experiments. CONCLUSION: Our analysis suggests that procedures that arrest cells in different stages of the cell cycle differentially affect expression of some cell cycle related genes once the cells are released from arrest. The impact of the cell-arresting method on expression of a cell cycle related gene can be quantitatively estimated from the ratio of two estimated amplitudes in two experiments. The ratio can be used to gauge the variation in the phase/peak expression time distribution involved in stochastic transcription and post-transcriptional processes for the gene. Further investigations are needed using normal, unperturbed and synchronized HeLa cells as a reference to compare how many cell cycle related genes are directly and indirectly affected by various cell-arresting methods.

Dose-response modeling in reproductive toxicology in the systems biology era.

Systems biology approaches for modeling cellular signaling networks affected by chemical exposures should soon produce integrated methodologies capable of predicting dose-response relationships for developmental toxicants and for other toxic responses. This paper outlines an emerging strategy for systems biology approaches in dose-response modeling. Genome-wide functional screens, bioinformatic tools, and network mapping technologies together can provide directed graph representations of the cellular signaling networks. The graphical representations can be converted into mathematical models that permit predicting the shapes of dose-response curves for altered cell signaling by test compounds during development. Systems biology approaches require interdisciplinary teams with expertise in reproduction, cell biology, signal transduction, mathematical/biomedical modeling, and risk assessment. In addition to outlining a systems approach for dose-response research, this paper discusses initial stages of application of this strategy to examine inhibition of steroidogenesis in testes by phthalate esters.

Di(n-butyl) phthalate impairs cholesterol transport and steroidogenesis in the fetal rat testis through a rapid and reversible mechanism.

In utero exposure to di(n-butyl) phthalate (DBP) leads to a variety of male reproductive abnormalities similar to those caused by androgen receptor antagonists. DBP demonstrates no affinity for the androgen receptor, but rather leads to diminished testosterone production by the fetal testis. The purpose of this study was to determine the onset and reversibility of DBP effects on the fetal testis and to determine at a functional level the points in the cholesterol transport and steroidogenesis pathways affected by DBP. Starting at gestational day (gd) 12, pregnant rats were gavaged daily with 500 mg/kg DBP or corn oil control. Significant decreases in testosterone production and mRNA expression of scavenger receptor B1, P450(SCC), steroidogenic acute regulatory protein, and cytochrome p450c17 were observed as early as gd 17. Testosterone, mRNA, and protein levels remained low 24 h after withdrawal of DBP treatment but increased 48 h after cessation of DBP exposure. In another experiment, pregnant dams were treated with DBP until gd 19, with the start of DBP treatment moved 1 d later into gestation for each treatment group, with the final group dosed only on gd 19. Significant decreases in testosterone, mRNA expression, and protein expression were evident as early as 3 h after treatment with DBP, with full repression apparent 24 h after treatment. Using a testis explant system, we determined that DBP treatment led to diminished transport of cholesterol across the mitochondrial membrane as well as diminished function at each point in the testosterone biosynthesis pathway except 17 beta-hydroxysteroid dehydrogenase. The transcriptional repression caused by DBP does not appear to be mediated via interference with steroidogenic factor-1 as determined by reporter assays. We conclude that high-dose DBP exposure leads to rapid and reversible diminution of the expression of several proteins required for cholesterol transport and steroidogenesis in the fetal testis, resulting in decreased testosterone synthesis and consequent male reproductive maldevelopment.

Interaction of organophosphate pesticides and related compounds with the androgen receptor.

Identification of several environmental chemicals capable of binding to the androgen receptor (AR) and interfering with its normal function has heightened concern about adverse effects across a broad spectrum of environmental chemicals. We previously demonstrated AR antagonist activity of the organophosphate (OP) pesticide fenitrothion. In this study, we characterized AR activity of analogues of fenitrothion to probe the structural requirements for AR activity among related chemicals. AR activity was measured using HepG2 human hepatoma cells transfected with human AR plus an androgen-responsive luciferase reporter gene, MMTV-luc. AR antagonist activity decreased as alkyl chain length of the phosphoester increased, whereas electron-donating properties of phenyl substituents of the tested compounds did not influence AR activity. Oxon derivatives of fenitrothion, which are more likely to undergo hydrolytic degradation, had no detectable AR antagonist activity. Molecular modeling results suggest that hydrogen-bond energies and the maximum achievable interatomic distance between two terminal H-bond capable sites may influence both the potential to interact with the AR and the nature of the interaction (agonist vs. antagonist) within this series of chemicals. This hypothesis is supported by the results of recent AR homology modeling and crystallographic studies relative to agonist- and antagonist-bound AR complexes. The present results are placed in the context of structure-activity knowledge derived from previous modeling studies as well as studies aimed toward designing nonsteroidal antiandrogen pharmaceuticals. Present results extend understanding of the structural requirements for AR activity to a new class of nonsteroidal, environmental, OP-related chemicals.

Dose-dependent alterations in gene expression and testosterone synthesis in the fetal testes of male rats exposed to di (n-butyl) phthalate.

Exposure to di (n-butyl) phthalate (DBP) in utero impairs the development of the male rat reproductive tract. The adverse effects are due in part to a coordinated decrease in expression of genes involved in cholesterol transport and steroidogenesis with a resultant reduction in testosterone production in the fetal testis. To determine the dose-response relationship for the effect of DBP on steroidogenesis in fetal rat testes, pregnant Sprague-Dawley rats received corn oil (vehicle control) or DBP (0.1, 1.0, 10, 50, 100, or 500 mg/kg/day) by gavage daily from gestation day (GD) 12 to 19. Testes were isolated on GD 19, and changes in gene and protein expression were quantified by RT-PCR and Western analysis. Fetal testicular testosterone concentration was determined by radioimmunoassay. DBP exposure resulted in significant dose-dependent reductions in mRNA and protein concentration of scavenger receptor, steroidogenic acute regulatory protein (StAR), cytochrome P450 side-chain cleavage, 3beta-hydroxysteroid dehydrogenase, and cytochrome P450c17. Testicular testosterone was reduced at doses of 50 mg/kg/day and above. Whole-testis expression of peripheral benzodiazepine receptor (PBR) mRNA, which functions with StAR to transport cholesterol across the mitochondrial membrane, was upregulated following exposure to DBP at 500 mg/kg/day. By immunocytochemistry, however, PBR protein was reduced in interstitial cells and also expressed but not reduced in gonocytes. Our results demonstrate a coordinate, dose-dependent reduction in the expression of key genes and proteins involved in cholesterol transport and steroidogenesis and a corresponding reduction in testosterone in fetal testes following maternal exposure to DBP, at dose levels below which adverse effects are detected in the developing male reproductive tract. Alterations in gene and protein expression and testosterone synthesis may serve as sensitive indicators of testicular response to DBP.

Quantitative changes in gene expression in fetal rat testes following exposure to di(n-butyl) phthalate.

Di(n-butyl) phthalate (DBP) alters male reproductive development by decreasing testicular testosterone (T) production when fetuses are exposed on gestation days (GD) 12-21. Previous studies have shown altered gene expression for enzymes in the T biosynthetic pathway following exposure to DBP. The objectives of this study were to develop a more detailed understanding of the effect of DBP on steroidogenesis, using a robust study design with increased numbers of dams and fetuses, compared with previous studies, and to explore messenger RNA (mRNA) expression for other critical genes involved in androgen biosynthesis and signaling. Additionally, immunohistochemical localization of protein expression for several key genes was performed to further confirm mRNA changes. Fetal Leydig cell lipid levels were also examined histochemically, using oil red O. Six to seven pregnant Crl:CD(SD)BR rats per group were gavaged with corn oil or DBP at 500 mg/kg/day on GD 12-19. Testicular RNA isolated from three randomly selected GD 19 fetuses per litter was used for real-time RT-PCR for the following genes: scavenger receptor class B-1 (SRB1), steroidogenic acute regulatory protein (StAR), P450 side-chain cleavage enzyme (P450scc), 3beta-hydroxysteroid dehydrogenase (3beta-HSD), P450c17, 17beta-hydroxysteroid dehydrogenase (17beta-HSD), androgen receptor (AR), luteinizing hormone receptor (LHR), follicle-stimulating hormone receptor (FSHR), stem cell factor tyrosine kinase receptor (c-kit), stem cell factor (SCF), proliferating cell nuclear antigen (PCNA), and testosterone-repressed prostate message-2 (TRPM-2). mRNA expression was downregulated for SRB1, StAR, P450scc, 3beta-HSD, P450c17, and c-kit following DBP exposure, and TRPM-2 was upregulated. 17beta-HSD, AR, LHR, FSHR, and PCNA were not significantly changed. Immunohistochemical staining for c-kit was seen in fetal Leydig cells, which has not been previously reported. Downregulation of most of the genes in the T biosynthetic pathway confirms and extends previous findings. Diminished Leydig cell lipid content and alteration of cholesterol transport genes also support altered cholesterol metabolism and transport as a potential mechanism for decreased T synthesis following exposure to DBP.

17beta-estradiol is a hormonal regulator of mirex tumor promotion sensitivity in mice.

Mirex, an organochlorine pesticide, is a potent non-phorbol ester tumor promoter in mouse skin. Previous studies have shown that female mice are 3 times more sensitive to mirex tumor promotion than male mice and that ovariectomized (OVX) female mice are resistant to mirex promotion, suggesting a role for ovarian hormones in mirex promotion. To determine whether the ovarian hormone 17-beta estradiol (E2) is responsible for the sensitivity of female mice to mirex promotion, female mice were initiated with DMBA; 2 weeks later groups of mice were OVX and implants, with or without E2, were surgically implanted subcutaneously. These mice were treated topically twice weekly with mirex for 26 weeks. E2 implanted OVX mice demonstrated high normal physiologic levels of serum E2 throughout the tumor promotion experiment. E2 implants restored by 80% the intact mirex-sensitive phenotype to the OVX mice. Consistent with a role for E2 and ERalpha and ERbeta, treatment of DMBA-initiated female mice with topical ICI 182,780, an estrogen-receptor antagonist, reduced mirex tumor multiplicity by 30%. However, in cells co-transfected with ERalpha or ERbeta and estrogen-responsive promoter reporter, mirex did not stimulate promoter reporter activity, suggesting that the promotion effect of mirex is downstream of ERalpha/beta. Finally, a tumor promotion study was conducted to determine whether E2 implants could increase the sensitivity of male mice to mirex promotion. E2 implants in male mice did increase sensitivity to mirex promotion; however, the implants did not produce the full female sensitivity to mirex tumor promotion. Collectively, these studies indicate that E2 is a major ovarian hormone responsible for mirex tumor promotion sensitivity in female mice.

Effects of in utero exposure to the organophosphate insecticide fenitrothion on androgen-dependent reproductive development in the Crl:CD(SD)BR rat.

Fenitrothion [0,0-dimethyl-O-(4-nitro-m-tolyl) phosphorothioate] is an organophosphate insecticide that has been shown to have antiandrogenic activity using in vitro and in vivo screening assays. Studies were performed to evaluate the ability of fenitrothion to disrupt androgen-dependent sexual differentiation in the male rat. Pregnant Crl:CD(SD)BR rats were administered fenitrothion by gavage at 0, 5, 10, 15, 20, or 25 mg/kg/day ( n = 6-11/group) from gestation day (GD) 12 to 21. Maternal toxicity was observed in the dams treated with 20 and 25 mg fenitrothion/kg/day based on muscle tremors and decreases in body weight gain from GD 12 to 21. Fetal death was increased in the 20 and 25 mg/kg/day exposure groups, as evidenced by a decrease in the proportion of pups born alive. Androgen-mediated development of the reproductive tract was altered in male offspring exposed in utero to maternally toxic levels of fenitrothion (25 mg/kg/day), as evidenced by reduction in anogenital distance on postnatal day (PND) 1 and retention of areolae on PND 13. However, these effects were only transient, and there were no indications of abnormal phenotypes or development of androgen-dependent tissues on PND 100. At the dose levels evaluated in this study, fenitrothion was only weakly antiandrogenic in vivo compared with other androgen receptor antagonists such as flutamide, linuron, and vinclozolin. Based on observed fetotoxicity at 20 mg/kg/day, the lowest observed adverse effect level (LOAEL) for developmental effects can be lowered from 25 to 20 mg/kg/day.

Combined effects of dietary phytoestrogen and synthetic endocrine-active compound on reproductive development in Sprague-Dawley rats: genistein and methoxychlor.

Humans and wildlife are frequently exposed to mixtures of endocrine active-compounds (EAC). The objective of the present study was to investigate the potential of the phytoestrogen genistein to influence the reproductive developmental toxicity of the endocrine-active pesticide methoxychlor. Three levels of genistein (0, 300, or 800 ppm) and two levels of methoxychlor (0 or 800 ppm) were used in this study. Sprague-Dawley rats were exposed to the two compounds, either alone or in combinations, through dietary administration to dams during pregnancy and lactation and to the offspring directly after weaning. Both compounds, methoxychlor in particular, were associated with reduced body growth at 800 ppm, but pregnancy outcome was not affected by either treatment. An acceleration of vaginal opening (VO) in the exposed female offspring was the only observed effect of genistein at 300 ppm. Exposure to 800 ppm genistein or 800 ppm methoxychlor caused accelerated VO and also altered estrous cyclicity toward persistent estrus in the female offspring. The estrogenic responses to genistein and methoxychlor administered together were apparently accumulative of the effects associated with each compound alone. Methoxychlor, but not genistein, delayed preputial separation (PPS) in the male rats. When administered with methoxychlor, genistein at 800 ppm enhanced the effect of methoxychlor on delaying PPS. Genistein and methoxychlor treatment did not change gender-specific motor activity patterns in either sex. To explore possible mechanisms for interaction between the two compounds on development, we performed estrogen receptor (ER)- and androgen receptor (AR)-based in vitro transcriptional activation assays using genistein and the primary methoxychlor metabolite 2,2-bis-(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE). While the in vitro assays supported the estrogenic effects of genistein and methoxychlor and the antiandrogenic effects of methoxychlor, the reactivity of these compounds with ERs alpha and beta could not predict the greater in vivo estrogenic potency of methoxychlor over genistein; nor could the potentiation of the methoxychlor effect on PPS by genistein be predicted based on in vitro HPTE and genistein reactions with the AR. Data from this study indicate that phytoestrogens are capable of altering the toxicological behaviors of other EACs, and the interactions of these compounds may involve complexities that are difficult to predict based on their in vitro steroid receptor reactivities.

Molecular alterations underlying the enhanced disruption of spermatogenesis by 2,5-hexanedione and carbendazim co-exposure.

The current study investigated the co-exposure effects of 2,5-hexanedione (HD) and carbendazim (CBZ) on gene expression underlying the enhanced pathology previously observed. Adult male rats were exposed to HD (0.33 or 1%) followed by CBZ (67 or 200 mg/kg), and testis samples were collected after 3 and 24 h. Microarray analysis at 3 h revealed that CBZ and HD interact in an agonistic, or synergistic, way at the gene level. Further analysis of candidate genes by qRT-PCR at both 3 and 24 h after co-exposure, revealed that Loxl1 and Clca2/Clca4l were both decreased in expression. Immunohistochemical analysis of Loxl1 at 24 h revealed that Loxl1 is localized to the seminiferous tubules, with the most intense staining in the basement membrane, blood vessels, and acrosomes, with the relative intensity reflecting the gene level changes at 3 h. These findings provide candidate genes for further investigation of the testicular response to damage.