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Embryonic exposure to the fungicide vinclozolin causes virilization of females and alteration of progesterone receptor expression in vivo: an experimental study in mice
Environmental Healthvolume 5, Article number: 4 (2006)
Vinclozolin is a fungicide that has been reported to have anti-androgenic effects in rats. We have found that in utero exposure to natural or synthetic progesterones can induce hypospadias in mice, and that the synthetic progesterone medroxyprogesterone acetate (MPA) feminizes male and virilizes female genital tubercles. In the current work, we selected a relatively low dose of vinclozolin to examine its in utero effects on the development of the genital tubercle, both at the morphological and molecular levels.
We gave pregnant dams vinclozolin by oral gavage from gestational days 13 through 17. We assessed the fetal genital tubercles from exposed fetuses at E19 to determine location of the urethral opening. After determination of gonadal sex, either genital tubercles were harvested for mRNA quantitation, or urethras were injected with a plastic resin for casting. We analyzed quantified mRNA levels between treated and untreated animals for mRNA levels of estrogen receptors α and β, progesterone receptor, and androgen receptor using nonparametric tests or ANOVA. To determine effects on urethral length (males have long urethras compared to females), we measured the lengths of the casts and performed ANOVA analysis on these data.
Our morphological results indicated that vinclozolin has morphological effects similar to those of MPA, feminizing males (hypospadias) and masculinizing females (longer urethras). Because these results reflected our MPA results, we investigated the effects of in utero vinclozolin exposure on the mRNA expression levels of androgen, estrogen α and β, and progesterone receptors. At the molecular level, vinclozolin down-regulated estrogen receptor α mRNA in females and up-regulated progesterone receptor mRNA. Vinclozolin-exposed males exhibited up-regulated estrogen receptor α and progesterone receptor mRNA, effects we have also seen with exposure to the synthetic estrogen, ethinyl estradiol.
The results suggest that vinclozolin virilizes females and directly or indirectly affects progesterone receptor expression. It also affects estrogen receptor expression in a sex-based manner. We found no in vivo effect of vinclozolin on androgen receptor expression. We propose that vinclozolin, which has been designated an anti-androgen, may also exert its effects by involving additional steroid-signaling pathways.
Vinclozolin has been identified as an anti-androgenic endocrine disruptor that produces malformations related to androgen inhibition in rats . This fungicide, used on food crops (soft fruits and vegetables) such as grapes used in wine , can be toxic in high doses, but its "no observed adverse effects level" is considered to be between 1 and 3 mg/kg in rats .
Vinclozolin is known to affect androgen-receptor-mediated endpoints [1, 4–8], but some research on behaviors inferred to be androgen-mediated indicates that progesterone receptors may also be involved in the manifestation of these behaviors since mice lacking the progesterone receptor exhibit alterations or decreases in these ostensibly androgen-mediated behaviors [9, 10]. Vinclozolin has been shown to affect androgen-receptor-mediated behaviors in mammals  and birds . In addition, research indicates an inability for vinclozolin to compete for androgen receptor in the fathead minnow , even though it disrupts male steroid profiles and alters female gonadal condition in adults . Although most of these studies are behavioral, they do imply the involvement of steroid receptors other than androgen receptors in these processes.
In a study with rats, androgen receptor mRNA was unaffected by vinclozolin exposure . Laws et al.  found that the two anti-androgenic metabolites of vinclozolin can compete with progesterone for progesterone receptor in vitro, but do not bind estrogen receptor. Their in vivo studies, however, indicated that vinclozolin did not disrupt progesterone-receptor-based pathways in adult animals; for example, it elicited no change in ovulation in adult female rats, and the researchers found no changes in progesterone receptor distribution after short-term vinclozolin exposure.
The study by Laws et al.  was performed using adult rats. Part of the endocrine-disruptor model is the choice of sensitive developmental time-points at which the organism may be most susceptible to exposure, especially to low-dose exposure (Crews et al. 2000). We investigated how a relatively low dose of vinclozolin affected fetal genital tubercle development in mice, a steroid-dependent process. Our results led us to conduct further investigations into the effects of in utero vinclozolin exposure on steroid receptor expression in the genital tubercle, especially progesterone receptor.
Materials and methods
Timed-pregnant CD1 mice were received on gestational day 8 (Charles River Laboratories, Wilmington, MA, USA) and housed in separate animal cages until embryonic stage (E) 13. All animals were housed one per cage (20 × 25 × 47 cm) with laboratory-grade pine shavings (heat-treated to remove resins) as bedding. They were acclimated to 68–74°F and 40%–50% relative humidity on a reversed light schedule (14 hr light and 10 hr dark) and received ad libitum mouse chow and water. All animal-related procedures described here were approved by our institutional animal care and use committee.
The pregnant mice were separated into three groups (N > 6 each); vehicle control (corn oil only), a low dose of vinclozolin (D1 = 10 mg/kg dissolved in corn oil), and a higher dose of vinclozolin (D2 = 50 mg/kg dissolved in corn oil). On gestational day (GD) 13 (the start of genital tubercle differentiation), we began daily gavaging of the pregnant mice with 0.1 ml of either corn oil (control), D1 vinclozolin, or D2 vinclozolin. Gavaging ended on gestational day 17. On GD 19, dams were killed by CO2 followed by cervical dislocation, and the fetuses were harvested via cesarean section and sex was determined by microscopic examination of gonads.
For casting, each fetal bladder/urethra was cast by injection (Baston's No. 17 Plastic Replica and Corrosion Kit (Polysciences, Inc., Warrington, PA, USA) using a 30 gauge needle with 3× microscopic visualization. The casting material was injected into the bladder until it emerged from the urethral opening. Casts set overnight at 4°C and were transferred to 20% potassium hydroxide the following day to dissolve the remaining tissue. The fetal bladder/urethra casts were photographed using a digital camera (Nikon 900, Melville, NY, USA). Using Adobe Photoshop 7.0 (Apple, Sunnyvale), we obtained fetal urethral measurements of urethral length based on pixel count. In the male pups, additional measurements were made from the prostate gland to Cowper's gland and from Cowper's gland to the distal urethral tip.
RT-PCR and macroscopic assessment of hypospadias
Timed pregnant CD1 mice (Charles River Breeding Laboratories, Wilmington, MA) were received on GD 8. Mice were gavaged once daily from GD 13 through 17 with 50 mg/kg vinclozolin or with corn oil alone as the vehicle control. We selected the dose of vinclozolin based on results published by Grey et al.4 showing that this was the lowest dose that elicited frank hypospadias in male rats exposed in utero; our goal for this set of experiments was to elicit hypospadias for molecular studies of the pathway. We also selected it based on preliminary investigations of our own indicating that this dose would produce hypospadias at a frequency that would allow us to compare tissue from hypospadic and nonhypospadic animals at the molecular level. All animals were housed as described above. Fetal genital tubercle morphology was assessed and tissue harvested on GD 19 (when urethral closure at the tip of genital tubercle normally has occurred) . Dams were killed by CO2 followed by cervical dislocation and fetuses removed. After gross examination and identification of the location of the urethral opening (either low or normal), gonadal sex was identified, and genital tubercles were harvested by microdissection and placed in RNAlater (Qiagen) for RNA isolation for RT-PCR analysis.
Visual assessment of urethra
Gross assessment of the location of the urethral opening was made primarily by expressing the bladder and observing the emergence of fluid; in normal E19 males, it emerges at the tip of the genital tubercle; in hypospadias it emerges more proximally.
Quantitative RT-PCR analysis
Total RNA from pooled tissues was extracted using a kit (Qiagen). It was reverse-transcribed to cDNA and quantitative RT-PCR analysis using the Taqman assay was performed at UCSF's Cancer Center Comprehensive Genome Analysis Core. Primers for the steroid receptors (the two estrogen receptors, progesterone receptor, and androgen receptor) were obtained commercially (Applied Biosystems, Foster City, CA). The gene expression assay used for progesterone receptor (Mm00435625) did not distinguish between the two isoforms; thus, quantification reflects expression of both PR-A and PR-B. Table 1 provides numbers of dams and pups and number of individuals per pooled sample of tissue analyzed. Data for receptor mRNA levels were normalized to the control gene, GapDH. This gene was chosen because it was shown to be the least variable under these experimental conditions (data not shown).
Statistical analyses were performed using JMP for PC. We used ANOVA analysis on the urethral cast length measurements. RT-PCR data, when not normally distributed, were analyzed and are reported based on a nonparametric median test; we also performed Grubb's outlier tests on RT-PCR data. For normally distributed RT-PCR data, we used ANOVA analysis.
Urethras from female E19 fetuses exposed to the higher dose of vinclozolin were significantly longer than the control female urethras (P = 0.005) (Fig. 1). In addition, the urethral lengths appeared to exhibit a dose response, with the female urethras from the lower-dose group exhibiting lengths intermediate to the control and higher-dose groups (Fig. 1). Urethras from female exposed to the lower dose of vinclozolin were not significantly longer than those from controls (P = 0.08).
The statistical analysis did not show any differences in urethral length among the males in the groups; however, visually, the urethras from vinclozolin-exposed males appeared considerably less robust and atrophic, and lacking in the typical "S" shape of a control urethra (Fig. 2).
Of the male genital tubercles examined macroscopically, we identified 8 of 59 (13.6%) as having hypospadias. None of the control male genital tubercles were identified as having hypospadias.
Vinclozolin-treated males had higher levels of progesterone receptor mRNA than control males (ANOVA, df = 1; F ratio = 14.1; P = 0.0016) (Fig. 3). In addition, vinclozolin-treated females had significantly higher levels of progesterone receptor mRNA in the genital tubercle (ANOVA, df = 1; F ratio = 52.07; P < 0.0001) (Fig. 3).
When we separated vinclozolin-treated males into two groups, those with and those without hypospadias, we found significant differences between each group compared to controls (P = 0.004 and P = 0.02, respectively) (not shown).
Control males and females did not differ in progesterone receptor mRNA expression (not shown).
Estrogen receptor α was significantly lower in vinclozolin-treated females (ANOVA, df = 1; F ratio = 58.86; P < 0.0001) (Fig. 4). In addition, vinclozolin-treated females exhibited lower levels of estrogen receptor β compared to controls (ANOVA, df = 1; F ratio = 7.62; P = 0.019) (not shown).
We found one outlier among the control males group (Grubb's outlier test) and removed it from the analysis. Estrogen receptor expression α was slightly significantly higher in vinclozolin-treated males than in control males (Wilcoxon's, df = 1; P = 0.03) (Fig. 4).
We found no significant changes in androgen receptor in comparisons among the groups.
Recent research suggests that compounds we believed were estrogenic may really be disrupting endocrine signaling via the progesterone receptor . Recently some progesterone disruptors have been identified in personal care products . In utero exposure to natural or synthetic progesterones can induce hypospadias in mice in which the urethral opening occurs more proximally than normal; the synthetic progesterone medroxyprogesterone acetate (MPA) feminizes male and virilizes female genital tubercles (EW et al. in preparation). In the current work, the relatively low dose of vinclozolin used caused hypospadias in the mice, but it also virilized the females, reflecting our findings with MPA. We also have observed a more proximal urethral opening in females treated with natural progesterone, but have not quantified these data (unpublished data).
Our morphological findings with vinclozolin, in the context of our findings with MPA and progesterone, led us to investigate the effects of vinclozolin on progesterone receptor expression, and on the expression of other steroid hormone receptors. In a study with rats, an in vitro assessment of the ability of two vinclozolin metabolites to bind progesterone receptor indicated that it could outcompete the natural ligand; however, the concordant in vivo studies from these investigations using adult male rats showed no in vivo effect . The discrepancy between these data and our current results could be attributable to species differences or differential responses based on timing of exposure. Our mice experienced vinclozolin exposure in utero, rather than as adults, and a central assumption of the endocrine-disruption model is that in utero exposures exert different and more powerful effects than do exposures in adults . In addition, our results are consistent between the morphological and molecular levels in males.
Vinclozolin-exposed males exhibited up-regulated estrogen receptor α and up-regulated progesterone receptor, effects we have also seen with exposure to the synthetic estrogen, ethinyl estradiol (unpublished data). Ethinyl estradiol up-regulates estrogen receptor α in females and upregulates progesterone receptor in both sexes. MPA also up-regulates estrogen receptor α and progesterone receptor in males, which it feminizes.
Vinclozolin can cause an increase in aromatase activity , which would presumably result in an increase in estradiol, especially in a system where testosterone is being made in abundance, as is the case with the male differentiation pathway. In fact, in the fathead minnow, a species that serves as a model of vertebrate endocrine disruption, vinclozolin exposure resulted in a slight increase in estradiol concentrations in adult male fish . Thus, vinclozolin could act on aromatase, which in turn could act on testosterone, both producing estradiol inappropriately and depriving 5-alpha-reductase of the substrate it needs to produce dihydrotesterone, the androgen necessary for appropriate male development of secondary sex characteristics. One possible explanation for the up-regulation of progesterone receptor mRNA in males could be the boosted estrogen receptor expression; estrogen receptor binds the progesterone receptor promoter. But another potential explanation, given the fact that vinclozolin binds progesterone receptor in vitro, is that it is affecting the receptor directly.
At the molecular level, vinclozolin down-regulated expression of estrogen receptors α and β in females and up-regulated progesterone receptor expression. Intuitively, the results with estrogen receptor suggest a lessening effect of estrogen, which would be consistent with our findings of virilization in the females. Androgen receptor expression remained unchanged in females. We speculate that the virilization that occurred in the female genital tubercle may have been the result of indirect estrogen antagonism; vinclozolin does not appear to be an estrogen receptor agonist or antagonist . It may enhance aromatase activity, and the up-regulation in aromatase activity may exhaust available substrate with the ultimate effect of lessening available estrogen. In addition, if signaling through the progesterone receptor is involved in the development of endpoints that are thought to be androgen-mediated, the increase in progesterone receptor in females may provide more opportunity for the development of these ostensibly androgen-associated phenotypes.
Our findings suggest that vinclozolin directly or indirectly affects progesterone receptor expression and that it also affects estrogen receptor expression in a sex-based manner. We found no in vivo effect of vinclozolin on androgen receptor expression in this tissue. We propose that vinclozolin, long designated as an anti-androgen, may also exert its effects by additional steroid-hormone signaling pathways.
lower dose of vinclozolin (10 mg/kg)
higher dose of vinclozolin (50 mg/kg)
Wolf CJ, LeBlanc GA, Ostby JS, Gray LE: Characterization of the period of sensitivity of fetal male sexual development to vinclozolin. Toxicol Sci. 2000, 55: 152-161. 10.1093/toxsci/55.1.152.
Cabras P, Angioni A: Pesticide residues in grapes, wine, and their processing products. J Agric Food Chem. 2000, 48: 967-973. 10.1021/jf990727a.
Hellwig J, van Ravenzwaay B, Mayer M, Gembardt C: Pre- and postnatal oral toxicity of vinclozolin in Wistar and Long-Evans rats. Reg Toxicol Pharmacol. 2000, 32: 42-50. 10.1006/rtph.2000.1400.
Gray LE, Ostby J, Monosson E, Kelce WR: Environmental androgens: low doses of the fungicide vinclozolin alter sexual differentiation of the male rat. Toxicol Ind Health. 1999, 15: 48-64. 10.1191/074823399678846646.
Kubota K, Ohsako S, Kurosawa S, Takeda K, Wu Q, Ishimura R, Tohyama C: Effects of vinclozolin administration on sperm production and testosterone biosynthetic pathway in adult male rat. J Reprod Dev. 2003, 49: 403-412. 10.1262/jrd.49.403.
Shono T, Suita S, Kai H, Yamaguchi Y: The effect of a prenatal androgen disruptor, vincolozolin, on gubernacular migration and testicular descent in rats. J Pedatr Surg. 2004, 39: 213-216. 10.1016/j.jpedsurg.2003.10.015.
Shono T, Suita S, Yamaguchi Y: Short-time exposure to vinclozolin in utero induces testicular maldescent associated with a spinal nucleus alteration of the genitofemoral nerve in rats. J Pediatr Surg. 2004, 39: 217-219. 10.1016/j.jpedsurg.2003.10.014.
Uzumcu M, Suzuki H, Skinner MK: Effect of the anti-androgenic endocrine disruptor vinclozolin on embryonic testis cord formation and postnatal testis development and function. Reprod Toxicol. 2004, 18: 765-774. 10.1016/j.reprotox.2004.05.008.
Phelps SM, Lydon J, O'Malley BW, Crews D: Regulation of male sexual behavior by progesterone receptor, sexual experience, and androgens. Horm Beh. 1998, 34: 294-302. 10.1006/hbeh.1998.1485.
Schneider JS, Stone MK, Wynne-Edwards KE, Horton TH, Lydon J, O'Malley B, Levine J: Progesterone receptors mediate male aggression toward infants. Proc Nat Acad Sci. 2003, 100: 2951-2956. 10.1073/pnas.0130100100.
Hotchkiss AK, Ostby JS, Vandenbergh JG, Gray LE: An environmental androgen, vinclozolin, alters organization of play behavior. Physiol Behav. 2003, 79: 151-156. 10.1016/S0031-9384(03)00093-3.
McGary S, Henry PFP, Ottinger MA: Impact of vinclozolin on reproductive behavior and endocrinology in Japanese quail (Coturnix coturnix japonica). Environ Toxicol Chem. 2001, 20: 2487-2493. 10.1897/1551-5028(2001)020<2487:IOVORB>2.0.CO;2.
Makynen EA, Kahl MD, Jensen KM, Tetge JE, Wells KL, Van der Kraak G, Ankley GT: Effects of the mammalian antiandrogen vinclozolin on development and reproduction of the fathead minnow (Pimephales promelas). Aquat Toxicol. 2000, 48: 461-475. 10.1016/S0166-445X(99)00059-4.
Laws SC, Carey SA, Kelce WR, Cooper RL, Gray LE: Vinclozolin does not alter progesterone receptor (PR) function in vivo despite inhibition of PR binding by its metabolites in vitro. Toxicol. 1996, 112: 173-182. 10.1016/0300-483X(96)03354-9.
Crews D, Willingham EJ, Skipper JK: Endocrine disruptors: Present issues, future problems. Q Rev Biol. 2000, 75: 243-260. 10.1086/393498.
Kim KS, Torres CR, Yucel S, Raimondo K, Cunha GR, Baskin LS: Induction of hypospadias in a murine model by maternal exposure to synthetic estrogens. Environ Res. 2004, 94: 267-275. 10.1016/S0013-9351(03)00085-9.
Scippo ML, Argiris C, Van De Weerdt C, Muller M, Willemsen P, Martial J, Maghuin-Rogester G: Recombinant human estrogen, androgen and progesterone receptors for detection of potential endocrine disruptors. Anal Bioanal Chem. 2003, 378: 664-669. 10.1007/s00216-003-2251-0.
Schreurs RHMM, Sonneveld E, Jansen JHJ, Seinen W, van der Burg B: Interaction of polycyclic musks and UV filters with the estrogen receptor (ER), androgen receptor (AR), and progesterone receptor (PR) in reporter gene bioassays. Toxicol Sci. 2005, 83: 264-272. 10.1093/toxsci/kfi035.
Sanderson JT, Boerma J, Lansbergen GW, van den Berg M: Induction and inhibition of aromatase (CYP19) activity by various classes of pesticides in H295R human adrenocortical carcinoma cells. Toxicol Appl Pharmacol. 2002, 182: 44-54. 10.1006/taap.2002.9420.
Kojima H, Katsura E, Takeuchi S, Niiyama K, Kobayashi K: Screening for estrogen and androgen receptor activities in 200 pesticides by in vitro reporter gene assays using Chinese hamster ovary cells. Environ Health Perspect. 2004, 112: 524-531.
This work was supported by NIH Grant RO1 DK058105-01. We thank UCSF's Cancer Center Core for their technical work with quantitative PCR.
The author(s) declare that they have no competing interests.
JB performed animal treatments, harvested tissue, performed casting, did casting measurements, and wrote portions of the paper. EW collaborated on experimental design, performed animal treatments, harvested tissue, performed the casting, analyzed the data, and wrote portions of the paper. KA treated mice, harvested and collected tissue for quantitative PCR, and performed RNA isolations. LB collaborated on experimental design, participated in data analysis, and wrote portions of the paper.