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W R Kelce

Publications and source records attributed to W R Kelce.

At least 19 recordsLinked to original sources
PubMed1999

Distinguishing androgen receptor agonists and antagonists: distinct mechanisms of activation by medroxyprogesterone acetate and dihydrotestosterone.

Natural and pharmacological androgen receptor (AR) ligands were tested for their ability to induce the AR NH2-terminal and carboxyl-terminal (N/C) interaction in a two-hybrid protein assay to determine whether N/C complex formation distinguishes in vivo AR agonists from antagonists. High-affinity agonists such as dihydrotestosterone, mibolerone, testosterone, and methyltrienolone at concentrations between 0.1 and 1 nM induce the N/C interaction more than 40-fold. The lower affinity anabolic steroids, oxandrolone and fluoxymesterone, require concentrations of 10-100 nM for up to 23-fold induction of the N/C interaction. However no N/C interaction was detected in the presence of the antagonists, hydroxyflutamide, cyproterone acetate, or RU56187, at concentrations up to 1 microM, or with 1 microM estradiol, progesterone, or medroxyprogesterone acetate; each of these steroids at 1-500 nM inhibited the dihydrotestosterone-induced N/C interaction, with medroxyprogesterone acetate being the most effective. In transient and stable cotransfection assays using the mouse mammary tumor virus reporter vector, all ligands displayed concentration-dependent AR agonist activity that paralleled induction of the N/C interaction, with antagonists and weaker agonists failing to induce the N/C interaction. AR dimerization and DNA binding in mobility shift assays and AR stabilization reflected, but were not dependent on, the N/C interaction. The results indicate that the N/C interaction facilitates agonist potency at low physiological ligand concentrations as detected in transcription, dimerization/DNA binding, and stabilization assays. However the N/C interaction is not required for agonist activity at sufficiently high ligand concentrations, nor does its inhibition imply antagonist activity.

Androgen Antagonists↗
PubMed1998

Antiandrogens as environmental endocrine disruptors.

Steroid hormone receptors control fundamental events in embryonic development and sex differentiation through their function as ligand-inducible transcription factors. The consequences of disrupting these processes can be especially profound during development due to the crucial role hormones play in controlling transient and irreversible developmental processes. Several environmental chemicals, including metabolites of the fungicide vinclozolin and the pesticide DDT, disrupt male reproductive development and function by inhibiting androgen receptor mediated events. A variety of in vitro and in vivo approaches have been used to determine the molecular basis of environmental antiandrogen toxicity. These chemicals commonly bind androgen receptor with moderate affinity and act as antagonists by inhibiting transcription of androgen dependent genes.

Androgen Antagonists↗
PubMed1997

Vinclozolin and p,p'-DDE alter androgen-dependent gene expression: in vivo confirmation of an androgen receptor-mediated mechanism.

Vinclozolin and p,p'-DDE induce antiandrogenic developmental effects in vivo and are potent inhibitors of androgen receptor (AR) binding and AR-dependent gene expression in vitro. To determine whether this molecular mechanism is operative in vivo, the effects of these compounds on two androgen-regulated prostatic mRNAs were studied. Rats were sham operated or castrated and immediately implanted with one or two empty 2.5-cm silastic capsules or with one (1x) or two (2x) 2.5-cm capsules containing testosterone (T). T-implanted rats were treated by gavage for 4 days with vehicle (corn oil), vinclozolin (200 mg/kg/day), p,p'-DDE (200 mg/kg/day), or the antiandrogen flutamide (100 mg/kg/day) as a positive control. Vinclozolin, p,p'-DDE, and flutamide all induced a reciprocal decline in seminal vesicle (p < 0.01) and prostate (p < 0.01) weight as well as a reduction in immunohistochemical staining of AR in epididymal nuclei compared to vehicle-treated T-implanted controls. Specific AR antagonism was assessed by determining the ability of these chemicals to induce a testosterone-repressed prostatic message (i.e., TRPM-2) and/or repress a testosterone-induced prostatic message (i.e., prostatein subunit C3). Densitometry scans of Northern blots indicated that vinclozolin, p,p'-DDE, and flutamide each induced TRPM-2 mRNA and repressed C3 mRNA compared to vehicle-treated T-implanted controls. These antiandrogenic effects were competitively reduced in castrate rats implanted with two 2.5-cm T capsules (2x), where serum T levels were elevated more than twofold above physiological levels. Taken together, these data indicate that vinclozolin and p,p'-DDE act as antiandrogens in vivo by altering the expression of androgen-dependent genes.

Androgen Antagonists↗
PubMed1997

A dose-response analysis of the reproductive effects of a single gestational dose of 2,3,7,8-tetrachlorodibenzo-p-dioxin in male Long Evans Hooded rat offspring.

Male rats exposed in utero to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) display reduced fertility as a consequence of the direct action of TCDD on the epididymides, as well as delayed puberty and altered reproductive organ weights. The current study provides dose-response data for the reproductive effects of TCDD, administered during pregnancy, with an emphasis on the effects of TCDD on testicular, epididymal, and ejaculated sperm numbers. Long Evans Hooded rats were dosed by gavage with 0, 0.05, 0.20, or 0.80 microg TCDD/kg on Day 15 of gestation. After birth, growth, viability, and developmental landmarks were monitored in both male and female offspring. Shortly after puberty (49 and 63 days of age) and at 15 months of age, male offspring were necropsied. Growth and viability of the pups were reduced only at 0.80 microg TCDD/kg, eye opening was accelerated (all dosage groups), and puberty was delayed (at 0.20 and 0.80 microg TCDD/kg). Treated progeny displayed transient reductions in ventral prostate and seminal vesicle weights, while epididymal sperm reserves and glans penis size were permanently reduced. Ejaculated sperm numbers were reduced (45% in the 0.8 and by 25% in the 0.05 and 0.2 microg TCDD/kg dosage groups) to a greater degree than were cauda or caput/corpus epididymal or testicular (unaffected) sperm numbers. In conclusion, administration of TCDD on Day 15 of pregnancy at 0.05 microg/kg altered eye opening and reduced ejaculated sperm counts, while higher dosage levels also delayed puberty and permanently reduced cauda epididymal sperm reserves.

Animals↗
PubMed1997

Environmental antiandrogens: developmental effects, molecular mechanisms, and clinical implications.

Industrial chemicals and environmental pollutants can disrupt reproductive development in wildlife and humans by mimicking or inhibiting the action of the gonadal steroid hormones, estradiol and testosterone. The toxicity of these so-called environmental endocrine disruptors is especially insidious during sex differentiation and development due to the crucial role of gonadal steroid hormones in regulating these processes. This review describes the mechanism of toxicity and clinical implications of a new class of environmental chemicals that inhibit androgen-mediated sex development. For several of these chemicals, including the agricultural fungicide vinclozolin and the ubiquitous and persistent 1,1,1-trichloro-2,2-bis (p-chlorophenyl)ethane metabolite, 1,1-dichloro-2,2-bis(p-chlorophenyl) ethylene, the molecular mechanism of action and the adverse developmental effects on male sex differentiation have been elucidated and are used as examples. Environmental chemicals with antiandrogenic activity offer profound implications with regard to recent clinical observations that suggest an increasing incidence of human male genital tract malformations, male infertility, and female breast cancer. Finally, in light of increasing concern over the potential endocrine disrupting effects of environmental pollutants, an in vitro/in vivo investigational strategy is presented which has proved useful in identifying chemicals with antiandrogen activity and their mechanism of action.

Androgen Antagonists↗
PubMed1996

Vinclozolin does not alter progesterone receptor (PR) function in vivo despite inhibition of PR binding by its metabolites in vitro.

Vinclozolin, a dicarboximide fungicide, alters morphological sex differentiation in male rats following perinatal exposure. The occurrence of these abnormalities correlates with the in vivo formation of two antiandrogenic metabolites of vinclozolin, (i.e. 2-[[(3,5-dichlorophenyl)-carbamoyl]oxy]-2-methyl-3-butenoic acid (Mt) and 3',5'-dichloro-2-hydroxy-2-methylbut-3-enanilide (M2)), which are potent inhibitors of rat androgen receptor binding. As steroid hormone receptors exhibit promiscuity in their ability to bind different ligands, the present study evaluated the ability of these vinclozolin metabolites to bind to the estrogen (ER) and progesterone (PR) receptors in vitro, and to alter ER and PR function following in vivo exposure. To this end, in vitro ligand binding assays demonstrated that both M1 and M2 can compete with endogenous ligand for binding to the PR (Ki = 400 and 60 microM, respectively). In contrast, neither metabolite exhibited the ability to bind ER. Subsequent in vivo studies to evaluate the potential of vinclozolin to alter ER or PR function demonstrate that, (1) the estrogen-dependent increases in uterine weight and PR induction were not altered by vinclozolin; (2) the distribution of nuclear and cytosolic PR was not altered following short-term vinclozolin exposure; and (3) vinclozolin did not disrupt ovulation in cycling female rats. These studies indicate that although vinclozolin metabolites can compete for binding to the PR in vitro, concentrations of these metabolites do not reach sufficient levels to disrupt female reproductive function following short-term in vivo exposure to vinclozolin. In addition, these studies demonstrate the importance of correlating in vitro receptor binding data with in vivo studies in order to understand the physiological consequences of exposure to environmental toxicants.

Anilides↗
PubMed1996

Endocrine modulation of reproduction.

The ability of foreign compounds to affect the functioning of various endocrine systems is currently thought responsible for a wide variety of effects. The presentations in this Symposium reviewed the evidence for and against the involvement of endocrine systems in several different aspects of reproduction. The mechanism behind the ability of a triazine herbicide to cause enhanced appearance of mammary tumors in one strain of female rats is reviewed by Stevens. The data suggest that enhanced aging, not direct mammary modulation, is responsible. Dietary phytoestrogens, the mediators of their actions, their effects in various biological systems, and the relationships between phytoestrogen producers and consumers are all provocatively and succinctly reviewed by Hughes. Kelce presents the strategy used to dissect the mode and mechanisms of action of a fungicide that opened a new awareness in reproductive toxicology: the possibility of xenobiotics being antiandrogens. Finally, to heighten our understanding of the interplay among hormonal systems in vivo, Hess reviews the data that show that androgens are not the only hormones important in the development of the male reproductive system: the pituitary is shown to play a critical role at specific stages of development. The breadth of these presentations, and the implications of their findings, should make us pause and realize how much there is still to discover about the interaction between the reproductive system and anthropogenic compounds.

Aging↗
PubMed1996

Three-dimensional quantitative structure--activity relationships for androgen receptor ligands.

Comparative molecular field analysis (CoMFA), a three-dimensional quantitative structure-activity relationship (3D-QSAR) paradigm, was used to examine androgen receptor-binding affinities of a series of structurally diverse natural, synthetic, and environmental chemicals of interest. The CoMFA/3D-QSAR model successfully illustrates that the overall steric and electrostatic properties of structurally diverse ligands for the androgen receptor are necessary and sufficient to describe the binding affinity. The practical utility of models of this type is demonstrated using parent compounds in the training set and known as well as putative biological metabolites as test set molecules. The ability of the model to accurately predict binding affinity of test set molecules suggests that structure-based 3D-QSAR models may be used to supplement the process of hazard identification. The application of 3D-QSAR models within a toxicological framework is, at present, limited by the quantity and quality of biological data for relevant biomarkers of toxicity.

Hazardous Substances↗
PubMed1996

Ligand-based identification of environmental estrogens.

Comparative molecular field analysis (CoMFA), a three-dimensional quantitative structure-activity relationship (3D-QSAR) paradigm, was used to examine the estrogen receptor (ER) binding affinities of a series of structurally diverse natural, synthetic, and environmental chemicals of interest. The CoMFA/3D-QSAR model is statistically robust and internally consistent, and successfully illustrates that the overall steric and electrostatic properties of structurally diverse ligands for the estrogen receptor are both necessary and sufficient to describe the binding affinity. The ability of the model to accurately predict the ER binding affinity of an external test set of molecules suggests that structure-based 3D-QSAR models may be used to supplement the process of endocrine disruptor identification through prioritization of novel compounds for bioassay. The general application of this 3D-QSAR model within a toxicological framework is, at present, limited only by the quantity and quality of biological data for relevant biomarkers of toxicity and hormonal responsiveness.

Animals↗
PubMed1996

Differential expression of glutathione S-transferase isoforms in compartments of the testis and segments of the epididymis of the rat.

Specific cell types of the mammalian testes demonstrate varying susceptibility to toxic insult by chemical agents. The mammalian testis is divided into two major compartments: seminiferous tubules, the site of spermatogenesis, and interstitium, which contains the Leydig cells. Glutathione S-transferase (GST) expression was examined in isolated compartments of the rat testis and in segments of the epididymis. Western blot analysis revealed the presence of GST class alpha, mu, and pi bands in each of the isolated compartments of the testis, and HPLC analysis of monomeric isoforms provided evidence for differential expression of multiple GST isoforms in testicular compartments. All major isoforms (e.g., forms 1, 2, 3, 4, 6, 7, 8, 9, and 11) were detected in the cytosol of whole testis. Isoform subunit 4 was the major form in the tubule, whereas isoform subunit 11 is the dominant form in the Leydig cells. Isoform subunits 3, 4, and 6 were enriched in the tubules as compared to interstitial or Leydig cells. The preferential action of reproductive toxicants at specific stages of aging may be due to an age-dependent expression of the activating or detoxifying enzymes in the reproductive tract. Therefore, the age-dependent expression of testicular GST isoforms was also examined. Expression of isoform subunits 2 and 4 displayed an age dependence, with the largest increase in these subunits occurring between ages 4 and 15 weeks. Isoform expression did not correlate with serum testosterone levels. HPLC analysis of the GST isoforms in the longitudinal segments of the epididymis and vas deferens revealed differential expression within these segments. Total GST protein and catalytic activity was highest in the caput epididymis and progressively decreased toward the vas deferens. Isoform subunit 2 was the major form expressed in the epididymis. The results of this study indicate that the GSTs are differentially expressed in testicular compartments and epididymal segments, and that this may contribute to susceptibility of different cell types to xenobiotic damage.

Animals↗
PubMed1995

Androgen receptor antagonist versus agonist activities of the fungicide vinclozolin relative to hydroxyflutamide.

The mechanism of antiandrogenic activity of vinclozolin (3-(3,5-dichlorophenyl)-5-methyl-5-vinyloxazolidine-2,4-dione), a dicarboximide fungicide under investigation for its potential adverse effects on human male reproduction, was investigated using recombinant human androgen receptor (AR). The two primary metabolites of vinclozolin in plants and mammals are M1 (2-[[3,5-dichlorophenyl)-carbamoyl]oxy]-2-methyl-3-butenoic acid) and M2 (3',5'-dichloro-2-hydroxy-2-methylbut-3-enanilide). Both metabolites, in a dose-dependent manner, target AR to the nucleus and inhibit androgen-induced transactivation mediated by the mouse mammary tumor virus promoter. M2 is a 50-fold more potent inhibitor than M1 and only 2-fold less than hydroxyflutamide. In the presence of dihydrotestosterone (50 nM), M2 (0.2-10 microM) inhibits androgen-induced AR binding to androgen response element DNA. In the absence of dihydrotestosterone, concentrations of 10 microM M2 or hydroxyflutamide promote AR binding to androgen response element DNA and activation of transcription. Agonist activities of M2 and hydroxyflutamide occur at 10-fold lower concentrations with the mutant AR (Thr877 to Ala) endogenous to LNCaP human prostate cancer cells. The results indicate that androgen antagonists can act as agonists, depending on ligand binding affinity, concentration, and the presence of competing natural ligands.

Androgen Receptor Antagonists↗
PubMed1995

Persistent DDT metabolite p,p'-DDE is a potent androgen receptor antagonist.

The increase in the number of reports of abnormalities in male sex development in wildlife and humans coincided with the introduction of 'oestrogenic' chemicals such as DDT (1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane) into the environment. Although these phenotypic alterations are thought to be mediated by the oestrogen receptor, they are also consistent with inhibition of androgen receptor-mediated events. Here we report that the major and persistent DDT metabolite, p,p'-DDE (1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene), has little ability to bind the oestrogen receptor, but inhibits androgen binding to the androgen receptor, androgen-induced transcriptional activity, and androgen action in developing, pubertal and adult male rats. The results suggest that abnormalities in male sex development induced by p,p'-DDE and related environmental chemicals may be mediated at the level of the androgen receptor.

Androgen Antagonists↗
PubMed1995

Exposure to TCDD during development permanently alters reproductive function in male Long Evans rats and hamsters: reduced ejaculated and epididymal sperm numbers and sex accessory gland weights in offspring with normal androgenic status.

Prenatal administration of relatively low doses of TCDD alters reproductive development and fertility of the progeny. Fertility was reduced in the progeny of Wistar rats exposed to 0.5 micrograms TCDD/kg/day from Gestational Day (GD) 6 to GD 15. In a three-generation reproduction study, TCDD reduced fertility of Sprague-Dawley rats in the F1 and F2 but not the F0 (no developmental exposure) generation at 0.01 microgram/kg/day in the diet. Furthermore, administration of TCDD on GD 15 (at 0.064 to 1 microgram/kg) both demasculinized and feminized morphology and behavior of Holtzman male rat offspring. Our objectives were to expand the observations of Mably et al. (1992, Toxicol, Appl. Pharmacol. 114, 97-107, 108-117, 118-126) on the effects of gestational administration of a single dose of TCDD to another strain of rat and another species, the hamster. In the first study, Long Evans (LE) hooded rats were dosed by gavage with 1 microgram TCDD/kg on GD 8 (during the period of major organogenesis) or GD 15 (the gestational day used by Mably et al.). In the second study, pregnant Syrian hamsters, a species relatively insensitive to the lethal effects of TCDD, were dosed on GD 11, equivalent to GD 15 in the rat, with TCDD at 2 micrograms/kg. When LE rats were dosed on GD 15, or when hamsters were dosed on GD 11, puberty (preputial separation) was delayed by about 3 days, ejaculated sperm counts were reduced by at least 58%, and epididymal sperm storage was reduced by 38%. Testicular sperm production was less affected. The sex accessory glands were also reduced in size in LE rat offspring treated on GD 15 despite the fact that serum testosterone (T), T production by the testis in vitro, and androgen receptor (AR) levels were not reduced. Some reproductive measures, such as anogenital distance and male sex behavior, were altered by TCDD treatment in rat but not hamster offspring. Since T and AR levels appeared normal in the sex accessory glands and the epididymis following perinatal TCDD exposure, the alterations in these tissues are not likely to have resulted from an alteration of the androgenic status of the male offspring.

Aging↗
PubMed1994

Distribution of [14C]ethane dimethanesulfonate in immature and adult male rats following an acute exposure.

In the adult rat, ethane dimethanesulfonate (EDS) reduces testosterone (T) production by killing Leydig cells. Studies have also shown that acute EDS administration produces transient infertility and epididymal effects. Although these later effects were believed to be indirect results of the reduced Leydig cell T production, it was recently found that the epididymal effects were partially a direct result of in vivo EDS treatment. In contrast to the Leydig cells of the adult rat, immature Leydig cells are affected by EDS only at doses four- to sixfold higher than those that affect mature Leydig cells. In fact, the Leydig cells of the adult rat seem to be uniquely susceptible to the cytotoxic effects of EDS. Steroidogenesis in other organs, like the adrenal and ovary, are unaffected in vivo at doses that eliminate T production in males. In addition, studies have shown that doses of EDS that kill Leydig cells in vitro, isolated from the testes of adult rats, have no effect on similarly exposed hepatocytes. Hence, it was the objective of this study to describe the distribution and temporal fate of EDS in target (testes and epididymides) and nontarget tissues in immature and adult male rats and to determine if this information would explain either the age- or tissue-related susceptibility to EDS. We have concluded from this study that tissue distribution, integrated in vivo EDS dose, and differences in EDS metabolism are not the only factors contributing to the difference in sensitivity.(ABSTRACT TRUNCATED AT 250 WORDS)

Aging↗
PubMed1994

Buthionine sulfoximine protects the viability of adult rat Leydig cells exposed to ethane dimethanesulfonate.

Exposure to (EDS) in vivo or in vitro alters adult rat Leydig cell function within 3 hr and these cells subsequently die within 24-48 hr. Previously, we determined that reducing intracellular glutathione levels with buthionine sulfoximine (BSO) protects adult rat Leydig cell function during short-term (3 hr) EDS exposures. The present study extends these observations by assessing whether BSO also can prevent Leydig cell death following EDS exposure. To assess whether BSO can prevent EDS-induced Leydig cell death, Leydig cells were cultured in the presence or the absence of 4 mM BSO (12 hr), and subsequently with increasing doses of EDS (3 hr). The effects of EDS on Leydig cell death were estimated using a cytotoxicity assay (MTT assay) and by assessing the ability of adult rat Leydig cells to maintain LH-stimulated testosterone production and [35S]methionine incorporation 24 hr following EDS exposure. This culture duration was chosen because sustained alterations in MTT reduction, LH-stimulated testosterone production, and [35S]methionine incorporation 24 hr following EDS exposure were found to reflect alterations in Leydig cell viability. The results suggest that lowering intracellular levels of glutathione with BSO prevents EDS-induced Leydig cell death. Restoring intracellular levels of glutathione with glutathione ethyl ester (8 mM) in the presence of BSO also restored the ability of EDS to kill Leydig cells. Taken together, these data suggest that glutathione mediates the mechanism by which EDS kills adult rat Leydig cells.

Animals↗
PubMed1994

Environmental hormone disruptors: evidence that vinclozolin developmental toxicity is mediated by antiandrogenic metabolites.

Recent studies with vinclozolin, a dicarboximide fungicide, demonstrate that perinatal exposure to 100 mg vinclozolin/kg/day from Gestational Day 14 through Postnatal Day 3 inhibits morphological sex differentiation. At 1 year, treated male rats exhibited hypospadias, cleft phallus, suprainguinal ectopic testes, a vaginal pouch, epididymal and testicular granulomas, and atrophic seminal vesicles and ventral prostate glands. This pattern of malformations suggests that this fungicide possesses antiandrogenic activity. To test this hypothesis, we examined the ability of vinclozolin to inhibit the conversion of testosterone to the more potent androgen 5 alpha-dihydrotestosterone via 5 alpha-reductase (EC 1.3.1.22) and to compete with androgen for binding to the androgen receptor. The results indicate that neither vinclozolin nor its degradation products, 2-[[(3,5-dichlorophenyl)-carbamoyl]oxy]-2-methyl-3-butenoic acid (M1) and 3',5'-dichloro-2-hydroxy-2-methylbut-3-enanilide (M2), inhibit 5 alpha-reductase activity. Although the ability of vinclozolin to compete with androgen for binding to the androgen receptor was weak (Ki > 700 microM), the two vinclozolin metabolites, M1 and M2, were effective antagonists of androgen receptor binding (Ki = 92 and 9.7 microM, respectively). As the concentrations of M1 in the serum of pregnant rats and their pups on Postnatal Day 3 meet or exceed the in vitro Ki for androgen receptor inhibition, we suggest that the demasculinizing effects of vinclozolin exposure in vivo also may be mediated via the antiandrogenic metabolites M1 and/or M2.

3-Oxo-5-alpha-Steroid 4-Dehydrogenase↗
PubMed1994

Developmental effects of an environmental antiandrogen: the fungicide vinclozolin alters sex differentiation of the male rat.

In humans and rodents, exposure to hormonally active chemicals during sex differentiation can produce a wide range of abnormal sexual phenotypes including masculinized and defeminized females and feminized and demasculinized males. Although numerous "environmental estrogens," including pesticides, toxic substances (PCBs), and plant and fungal estrogens, have been shown to alter mammalian sex differentiation, similar information on environmental androgens is lacking. Recently, the fungicide vinclozolin (V) was found to inhibit sexual differentiation in male rats in an antiandrogenic manner. In the present study, V was administered to pregnant rats (p.o.) at 0, 100, or 200 mg/kg/day in corn oil during the period of sex differentiation (Gestational Day 14 to Postnatal Day 3) to examine the demasculinizing effect of this fungicide more closely. In both groups of V-treated male offspring, anogenital distance was female like at birth, and nipple development was prominent at 2 weeks of age. After puberty, most of the V-treated male offspring were unable to attain intromission even though they all mounted sexually receptive females. The V-treated male offspring that appeared to achieve intromission, failed to ejaculate normally, as no sperm were found in the uterus after overnight matings. A factor in the abnormal ejaculation was that all V-treated male offspring had cleft phallus with hypospadias. In addition, a number of unusual reproductive malformations were noted when the males were necropsied at 1 year. Many V-treated male offspring had suprainguinal ectopic scrota/testes, a vaginal pouch, epididymal granulomas, and small to absent sex accessory glands. During the study, about 25% of the V-treated males died as a result of bladder stones, hydroureter, or hydronephrosis, while other males displayed these lesions at necropsy. While some of the above malformations in male offspring can also be produced by perinatal administration of a potent estrogen, like DES, V-treated female offspring did not display any estrogen-like alterations of reproductive development or fecundity. The only change seen in the female offspring was a reduced anogenital distance during neonatal life. Our observation of perinatal-induced agenesis of the prostate and blocked testicular descent, a pattern of malformations nearly identical to that reported for the antiandrogen flutamide, is consistent with other recent evidence that this fungicide is an androgen-receptor antagonist.

Administration, Oral↗