Comparative anti-androgenic actions of vinclozolin and flutamide on transgenerational adult onset disease and spermatogenesis

Exposure of gestating female rats to the anti-androgenic endocrine disruptor vinclozolin has been shown to induce transgenerational adult onset disease phenotypes. The current study, was designed to compare the actions of vinclozolin to the known anti-androgenic compound flutamide. The gestating female rats were exposed to intraperitoneal injections during embryonic day 8-14 (E8-E14) to 100mg/kg/day vinclozolin or flutamide at either 5mg or 20mg/kg/day. As previously observed, vinclozolin induced a transgenerational testis phenotype of increased spermatogenic cell apoptosis and decreased epididymal sperm number. In contrast, the flutamide exposures resulted in a testis phenotype of increased spermatogenic cell apoptosis and decreased epididymal sperm numbers in the F1 generation only, and not the F2 and F3 generation adult males. Interestingly, some of the low dose (5mg/kg) flutamide F2 generation offspring developed spinal agenesis and supernummery development (polymelia) of limbs. Although the actions of vinclozolin and flutamide appear similar in the F1 generation males, the transgenerational effects of vinclozolin do not appear to be acting through the same anti-androgenic mechanism as flutamide.     

Repeated in utero and lactational 2,3,7,8-tetrachlorodibenzo-p-dioxin exposure affects male gonads in offspring, leading to sex ratio changes in F2 progeny

The effects of in utero and lactational 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on the reproductive system of male rat offspring (F1) and the sex ratio of the subsequent generation (F2) were examined. Female Holtzman rats were gavaged with an initial loading dose of 400 ng/kg TCDD prior to mating, followed by weekly maintenance doses of 80 ng/kg during mating, pregnancy, and the lactation period. Maternal exposure to TCDD had no significant effects on fetus/pup (F1) mortality, litter size, or sex ratio on gestation day (GD) 20 or postnatal day (PND) 2. The TCDD concentration in maternal livers and adipose tissue on GD20 was 1.21 and 1.81 ng/kg, respectively, and decreased at weaning to 0.72 in the liver and 0.84 in the adipose tissue. In contrast, the TCDD concentration in pup livers was 1.32 ng/kg on PND2 and increased to 1.80 ng/kg at weaning. Ventral prostate weight of male offspring was significantly decreased by TCDD exposure on PND28 and 120 compared with that of controls. Weight of the testes, cauda epididymides, and seminal vesicle, and sperm number in the cauda epididymis were not changed by TCDD exposure at PND120. TCDD- or vehicle-exposed male offspring were mated with unexposed females. The sex ratio (percentage of male pups) of F2 offspring was significantly reduced in the TCDD-exposed group compared with controls. These results suggest that in utero and lactational TCDD exposures affect the development of male gonads in offspring (F1), leading to changes in the sex ratio of the subsequent generation (F2).     

Vinclozolin--the lack of a transgenerational effect after oral maternal exposure during organogenesis

The purpose of the study was to investigate a possible transgenerational effect of the fungicide vinclozolin on the male reproductive system following oral exposure since this effect was reported by Anway et al. [Anway MD, Cupp AS, Uzumcu M, Skinner MK. Epigenetic transgenerational actions of endocrine disruptors and male fertility. Science 2005;308(5727 (June 3)):1466-9] after intraperitoneal administration. Pregnant Wistar rats were dosed by oral gavage with vinclozolin 0, 4 or 100mg/(kg bw day) on days 6-15 post coitum (p.c.). F1 male offspring was mated with untreated females to produce F2, which were then similarly mated to produce F3 offspring. F0 maternal treatment had no effect on mating and fertility indices or male offspring sexual development, mean sperm parameters, or histopathology of the sexual organs in F1, F2 or F3 males (at age 127-134 days). Apoptotic germ cell counts were statistically significantly lower in F1, F2 and F3 generations, however, control values showed a pronounced variance over time. Also, as anti-androgenic compounds are more likely to induce the opposite effect (increased apoptosis), this observation is not considered to be treatment related. Consequently, spermatogenesis was not affected by vinclozolin exposure in utero. As vinclozolin has been shown to induce clear anti-androgenic effects in offspring following treatment with 100mg/(kg bw day) during entire gestation, the lack of effects in this study indicates that the window of sensitivity for anti-androgenic effects is from days 16-20 p.c. No transgenerational effect on the male reproductive system was found. The NOAEL was >100mg/(kg bw day) for fertility and reproductive performance, for systemic parental and developmental toxicity in F1, F2 and F3 males.     

Vinclozolin—No transgenerational inheritance of anti-androgenic effects after maternal exposure during organogenesis via the intraperitoneal route

The goal of this study was to examine the potential transgenerational inheritance of anti-androgenic effects induced by Vinclozolin administered intraperitoneally to pregnant Wistar rats (Crl:WI[Han]). Dams were dosed with Vinclozolin at 0, 4 or 100 mg/kg bw/d on gestation days 6–15. Male offspring of F1–F3 generations were bred with untreated females to yield F2–F4 offspring. No evident anti-androgenic effects were observed at 4 mg/kg bw/d, but a case of hypospadias as well as delayed sexual maturation in F1 male offspring was observed as a sign of anti-androgenicity at 100 mg/kg bw/d. However, F1–F3 males developed normally to sexual maturity and were able to mate and to generate healthy progeny. Sperm count, morphology and motility were not affected in F1–F4 generation male offspring. In conclusion, transgenerational inheritance of Vinclozolin's anti-androgenic effects was not evident in outbred Wistar rats.     

Long-lasting effects of lindane on mouse spermatogenesis induced by in utero exposure

Long-lasting effects on mouse spermatogenesis induced by prenatal exposure to the insecticide lindane have been investigated by conventional reproductive endpoints complemented by the flow cytometric (FCM) DNA content analysis of testis cells and by the Sperm Chromatin Structure Assay (SCSA). Two lindane dose levels, 15 and 25 mg/kg bw, and diethylstilboestrol (DES, 10 microg/kg bw) as positive control, were administered daily by gavage to pregnant CD1 mice on gestation days (GD) 9-16. Reproductive endpoints were evaluated on F1 male mice on postnatal day (PND) 60; additionally, animals treated with lindane 25 mg/kg per day and DES were examined on PND 100 to evaluate the possible reversibility of the effects. On PND 60, lindane and DES caused a reduction in the sperm head count and concentration, with recovery in older lindane 25 mg/kg per day animals (PND 100). By contrast, the DES group exhibited a greater reduction in the sperm head count on PND 100 than on PND 60. Changes in biochemical parameters in the testes, lactate dehydrogenase-C(4) (LDH-C(4)), and sorbitol dehydrogenase (SDH) activities, were also observed in adult treated F1 mice. Furthermore on PND 60, the FCM analysis revealed changes in the pattern of testicular germ cell distribution, especially in the haploid subcompartment, in the lindane 25 mg/kg per day group. A dose-dependent increase in chromatin abnormalities of the epididymal sperm was also shown by SCSA. These changes recovered on PND 100. Preliminary qualitative examination did not reveal any significant difference in the structure of testicular tissue; however, there were suggestions of a moderate increase in number and size of Leydig cells in both DES- and lindane-treated animals. The partial reversibility of these effects and the lack of structural modification of the testicular tissue as evidenced by histopathologic assessment suggest a functional impairment of sperm production and maturation, possibly associated with changes induced by lindane on factors affecting intratesticular steroidogenesis.     

Developmental toxicity of perfluorooctane sulfonate (PFOS) is not dependent on expression of peroxisome proliferator activated receptor-alpha (PPARα) in the mouse

Perfluorooctane sulfonate (PFOS) and perfluorooctanoic acid (PFOA) are members of a family of perfluorinated compounds. Both are environmentally persistent and found in the serum of wildlife and humans. PFOS and PFOA are developmentally toxic in laboratory rodents. Exposure to these chemicals in utero delays development and reduces postnatal survival and growth. Exposure to PFOS on the last 4 days of gestation in the rat is sufficient to reduce neonatal survival. PFOS and PFOA are weak agonists of peroxisome proliferator activated receptor-alpha (PPARα). The reduced postnatal survival of neonatal mice exposed to PFOA was recently shown to depend on expression of PPARα. This study used PPARα knockout (KO) and 129S1/SvlmJ wild type (WT) mice to determine if PPARα expression is required for the developmental toxicity of PFOS. After mating overnight, the next day was designated gestation day (GD) 0. WT females were weighed and dosed orally from GD15 to 18 with 0.5% Tween-20, 4.5, 6.5, 8.5, or 10.5 mg PFOS/kg/day. KO females were dosed with 0.5% Tween-20, 8.5 or 10.5 mg PFOS/kg/day. Dams and pups were observed daily and pups were weighed on postnatal day (PND) 1 and PND15. Eye opening was recorded from PND12 to 15. Dams and pups were killed on PND15, body and liver weights recorded, and serum collected. PFOS did not affect maternal weight gain or body or liver weights of the dams on PND15. Neonatal survival (PND1–15) was significantly reduced by PFOS in both WT and KO litters at all doses. WT and KO pup birth weight and weight gain from PND1 to 15 were not significantly affected by PFOS exposure. Relative liver weight of WT and KO pups was significantly increased by the 10.5 mg/kg dose. Eye opening of PFOS-exposed pups was slightly delayed in WT and KO on PND13 or 14, respectively. Because results in WT and KO were comparable, it is concluded that PFOS-induced neonatal lethality and delayed eye opening are not dependent on activation of PPARα.     

Effect of in utero and lactational exposure of triazophos on reproductive system functions in male offsprings,Rattus norvegicus

In the present study, Triazophos (TZ) was used at acceptable daily intake (ADI) to investigate the consequence of prenatal and postnatal exposure on reproductive functions in the male offsprings. Pregnant females were divided into three groups, the first group was orally gavaged with olive oil (control), the second group was administered with 0.01?mg kg^?1 bw of the ADI of TZ from gestation day (GD) 1 until parturition (designated as P group) and the third group was gavaged with the same dose from GD1 to postnatal day (PND) 21 of lactation (marked as P?+?L group). Non-significant reduction occurred in the body weight of pups except at (PND) 35 during which body weight of P?+?L group pups significantly decreased. Male offsprings born to TZ exposed females showed significant changes at maturity (PND 63) in weight of liver, thyroid and testis, alterations in the levels of protein, urea, creatinine in plasma and abnormal levels of cholesterol, phospholipids and lipid peroxidation in testicular homogenate. Gonadal inhibition in TZ exposed progeny was reflected from a significant fall in sperm count, sperm motility, plasma testosterone level and histopathological alterations in testis. Hence, in utero and lactational exposure to ADI level of TZ influences testis development and functions in the male offsprings. Further investigations are suggested with germline studies of offsprings to examine the transgenerational effect of TZ exposure.     

Effects of maternal exposure to di-n-butyl phthalate during pregnancy and breastfeeding on ovarian development and function of F1 female rats

This study aimed to investigate the effects of maternal exposure to di-n-butyl phthalate (DBP) during pregnancy and breastfeeding on F1 ovarian development and function. A rat model of maternal exposure to DBP during pregnancy and breastfeeding was established by gavage feeding female Sprague Dawley rats with 0, 10, 100, or 600 mg/kg/day DBP from gestational day (GD) 12 to postnatal day (PND) 21. F1 offspring were weaned on PND21 and were not exposed to DBP afterward. The age of vaginal opening and estrus onset, estrous cyclicity, c-Kit-ligand expression on ovarian granulosa cells, and the weight of ovaries and uterus of F1 female offspring were not affected, whereas serum levels of estradiol and progesterone were increased significantly by maternal exposure to 10 mg/kg/day DBP from GD12 to PND21. Although F1 ovarian function may not be adversely affected by maternal exposure to DBP, the increased reproductive hormone levels may interfere in F1 rat fertility.     

Impairment of male rat reproductive function in F1 offspring from dams exposed to 2-bromopropane during gestation and lactation

The toxic effects of 2-bromopropane (2-BP) on the reproductive tracts of male F1 offspring from dams exposed to 2-BP during gestation and lactation were investigated. Ten pregnant (sperm-positive) Sprague-Dawley rats per group were exposed sc to 2-BP at 135, 405, and 1215 mg/kg/day from gestation day (GD) 6 to postnatal day (PND) 20. 2-BP decreased the proportion of dams littering at the two highest doses. At the highest dose, the rate of delivery and surviving pups were significantly lower than in the controls (P < or = 0.05). The relative weights of testes vs. brain were significantly lower than the controls (P < or = 0.05) on PND 33 and 63 at 405 mg/kg/day, and on PND 90 at 1215 mg/kg/day in the F1 rats. Seminiferous tubule atrophy, germ cell loss, and increased Leydig cell proliferation were observed at the highest dose by histopathologic examination. Female offspring has a decrease in all follicle types at the high dose. These results suggest that gestational and lactational exposure to 2-BP at a high maternally toxic dose impairs the development of the reproductive organs of the offspring.     

Fertility and early embryonic development toxicity of penequine hydrochloride in mice.

Penequine hydrochloride, a novel anticholinergic agent, was developed as an effective treatment for organophosphorus intoxication. The potential for penequine hydrochloride to induce fertility and early embryonic developmental toxicity was evaluated in AMMS-1 mice. Totally 320 healthy, sexual mature and nulliparous AMMS-1 mice were orally treated with the chemical in drinking water at dose levels of 0, 2.5, 12.5 and 62.5 mg/L from 60 days before cohabitation to successful copulation in 160 males and from two weeks before cohabitation to GD 6 in 160 females, respectively. All the parental mice were observed for body weights, water consumption and any abnormal change during treatment period. Caesarean sections were carried out on day 14 of pregnancy in half assumed-pregnant females, and all the intrauterine data were recorded. Pups naturally delivered by the other half females were weighed, and examined for viability, sex ratio and gross malformations. About 7 days after cohabitation period, all the paternal males were examined for epididymal and testicular weights, sperm number and sperm motility. The decreases in fertility/fecundity indices and maternal weight gain were found at high-dose level in both caesarean sections and natural delivery observations. The primary developmental toxicity of the chemical included decreases in relative organ (epididymis, liver and lung) weights at mid- and high-dose levels in pups on postnatal day (PND) 35. The cause of both the decreased fertility/fecundity indices in F0 males and the decreased relative organ weights in F1 pups are not well known but are presently under investigation. Under the experimental conditions, penequine hydrochloride did not produce any adverse effects (expect the decreases in certain relative organ weights) up to and including 12.5 mg/L (2.53 mg/kg/day in males and 2.19 mg/kg/day in females) corresponding to approximately 72 times above anticipated dosage in human.     

Developmental toxicology of trimethyltin in the rat

Pregnant rats were treated on either gestational day (GD) 7, 12, or 17 with single doses of trimethyltin chloride (TMT) ip at either 0, 5, 7, or 9 mg/kg. A significant effect of dose was manifest as decreased maternal weight at term, which persisted during lactation until postnatal day (PND) 15 in some groups. For all treatments combined, term weights of dams exposed on GDs 7 and 12 were greater than those treated on GD 17. Litter sizes were decreased for groups treated on GD 17 with 9 mg/kg TMT. Pups treated in utero and exhibiting treatment-induced decreases in weight at or near birth remained smaller than untreated animals into adulthood (PND 280). By PND 20, weights of pups treated on GD 7 greater than GD 12 greater than GD 17. Neuropathology of pups sacrificed on PND 1 was minimal in all animals with lesions only identified in animals treated on GDs 12 or 17 which consisted of subtle degenerative changes in the CA3 and CA4 regions of Ammon's horn of the hippocampus. Muscarinic cholinergic receptor binding in whole brains from pups on PND 1 did not show any significant changes compared to controls for any dose or day of exposure. These data indicate that prenatal TMT exposure results in postnatal toxicity in treated pups but only in the presence of maternal toxicity.     

Lactational fenvalerate exposure permanently impairs testicular development and spermatogenesis in mice

Fenvalerate, a widely used synthetic pyrethroid insecticide, has been associated with poor semen quality in human being. However, little is known about the effects of lactational fenvalerate exposure on testicular development and spermatogenesis. The purpose of the present study was to investigate the effects of maternal fenvalerate exposure during lactation on testicular development and spermatogenesis in male offspring. Maternal mice were administered with fenvalerate (60 mg/kg) by gavage daily from postnatal day (PND) 0 to PND21. Lactational fenvalerate exposure markedly decreased the absolute and relative weights of testes and increased the number of apoptotic cells in testes of pups at weaning. Histological examinations showed abnormal seminiferous tubules with large vacuoles or complete spermatogenic failure in testes of fenvalerate-treated mice at weaning. Additional experiment showed that lactational fenvalerate exposure markedly reduced mRNA and protein levels of testicular P450scc, a testosterone (T) synthesis enzyme. Consistent with down-regulation of testicular P450scc, the level of serum and testicular T at weaning was significantly decreased in pups whose mothers were exposed to fenvalerate during lactation. Although the expression of testicular P450scc and serum and testicular T in adulthood restored to control level, the decreased weight of testes and histological changes were irreversible. Importantly, the percentage of mature seminiferous tubules (stages VII and VIII) and the number of spermatozoa were obviously decreased in adult male mice whose mothers were exposed to fenvalerate during lactation. Taken together, these results suggest that lactational fenvalerate exposure permanently impairs testicular development and spermatogenesis.     

Vinclozolin: A feasibility and sensitivity study of the ILSI-HESI F1-extended one-generation rat reproduction protocol

Feasibility of the ILSI-HESI (ACSA) extended one-generation protocol was tested with vinclozolin (dietary 0, 4, 20, 100 mg/kg/day). Parental Wistar rats (n = 25/sex/dose) were dosed pre-mating (males 4, females 2 weeks) through F1 offspring weaning (postnatal day PND21); F1 dosing continued through PND70. At PND21, 3 subsets (each 1 pup/sex/litter) were selected for neurotoxicology (functional observational battery, motor activity, neuropathology), clinical pathology (hematology, clinical chemistry, urinalysis, thyroid hormone assay) (subsets 1a, 1b; each n = 10/sex/dose), immunotoxicology (IgM) SRBC antibody response and natural killer cell assays (subset 2; n = 25/sex/dose), and estrus cycle (subset 3; n = 25/dose). Vinclozolin reduced parental and offspring bodyweight and prostate, seminal vesicles and epididymides weight, and increased adrenal weight/induced adrenal cortical hypertrophy at 100 mg/kg. Mating, fertility, gestation and lactation were unaffected. At 20 and 100 mg/kg, F1 males had reduced anogenital distance and retained areolae; at 100 mg/kg only, there was hypospadias, purulent prostatitis and seminal vesicle inflammation with atrophy, and Leydig cell hyperplasia, and in F1 females accelerated vaginal opening. These effects are consistent with vinclozolin’s known anti-androgenic developmental effects. Neuro- and immunotoxicology tests were unaffected. F1 Only T4 was reduced at 20 and 100 mg/kg. The overall sensitivity of the extended one-generation protocol is comparable to or even greater than the current two-generation study. Thus it reduces animal use while maintaining or enhancing information for risk assessment.     

Preweaning behaviors,developmental landmarks,and acrylamide and glycidamide levels after pre- and postnatal acrylamide treatment in rats

At high levels of exposure, acrylamide monomer (AA) is a known neurotoxicant (LoPachin, 2004 [23]). The effects of lower levels of exposure, such as those experienced via a typical human diet, have not been widely investigated. Data at these levels are particularly relevant given the widespread human exposure through carbohydrate-containing foods cooked at high temperatures. Additionally, daily AA intake is estimated to be higher for infants and children. Earlier, we described behavioral alterations in preweaning rats resulting from developmental AA treatment (0.5–10.0 mg/kg/day) (Garey et al., 2005 [14]). In the present study, the effects of lower doses were measured as well as serum AA and glycidimide (GA) levels in dams, fetuses, and young pups. Pregnant Fischer 344 dams (n = 48–58/treatment group) were gavaged with 0.0, 0.1, 0.3, 1.0, or 5.0 mg AA/kg/day beginning on gestational day 6 and ending on the day of parturition. Beginning on postnatal day 1 (PND 1) and continuing through PND 21, all pups/litter were gavaged with the same dose as their dam. There were no AA treatment effects on offspring fur development, pinnae detachment, or eye opening. Offspring body weight was somewhat decreased by 5.0 mg/kg/day, particularly in males. However, righting reflex (PNDs 4–7), slant board (i.e., negative geotaxis) (PNDs 8–10), forelimb hang (PNDs 12–16), and rotarod behavior (PNDs 21–22) were not significantly altered by AA treatment. Male and female offspring of the 5.0 mg/kg/day group were 30–49% less active in the open field at PNDs 19–20 (p < 0.05). Serum AA levels of GD20 dams and their fetuses were comparable, indicating the ability of AA to cross the placental barrier. AA levels of pups were not affected by age (PND 1 and 22) or sex. In all rats, serum AA and GA levels exhibited a dose–response relationship. These data extend those of our previous study (Garey et al., 2005 [14]) and demonstrate that overt preweaning neurobehavioral effects are apparent in rats exposed to acrylamide pre- and postnatally, but only at the highest doses tested.     

Reproductive and behavioral effects of diisononyl phthalate (DINP) in perinatally exposed rats

Diisononyl phthalate (DINP) is a plasticizer abundantly used in consumer products as a substitute for other plasticizers prohibited in certain products due to reproductive toxicity. As anti-androgenic effects of DINP are suspected, DINP effects on reproduction and sexually dimorphic behavior were studied. Pregnant Wistar rats were gavaged from gestation day 7 to postnatal day (PND) 17 with vehicle, 300, 600, 750 or 900 mg DINP/kg bw/day. In fetal testes histopathological effects typical of phthalates were observed. In male offspring, DINP caused increased nipple retention, reduced anogenital distance, reduced sperm motility and increased sperm count. DINP affected spatial learning as female offspring performed better than controls and similarly to control males in the Morris Water Maze, indicating masculinization of behavior in DINP exposed females. These results show that DINP causes anti-androgenic effects on reproductive development, though less potent than DEHP, DBP and BBP, and further safety evaluation of DINP appears warranted.     

Three-generation reproductive toxicity study of dietary bisphenol A in CD Sprague-Dawley rats.

Bisphenol A (BPA) was evaluated at concentrations of 0, 0.015, 0.3, 4.5, 75, 750, and 7500 ppm ( approximately 0.001, 0.02, 0.3, 5, 50, and 500 mg/kg/day of BPA) administered in the diet ad libitum to 30 CD((R)) Sprague-Dawley rats/sex/dose for 3 offspring generations, 1 litter/generation, through F3 adults. Adult systemic toxicity at 750 and 7500 ppm in all generations included: reduced body weights and body weight gains, reduced absolute and increased relative weanling and adult organ weights (liver, kidneys, adrenals, spleen, pituitary, and brain), and female slight/mild renal and hepatic pathology at 7500 ppm. Reproductive organ histopathology and function were unaffected. Ovarian weights as well as total pups and live pups/litter on postnatal day (PND) 0 were decreased at 7500 ppm, which exceeded the adult maximum tolerated dose (MTD). Mating, fertility, gestational indices; ovarian primordial follicle counts; estrous cyclicity; precoital interval; gestational length; offspring sex ratios; postnatal survival; nipple/areolae retention in preweanling males; epididymal sperm number, motility, morphology; daily sperm production (DSP), and efficiency of DSP were all unaffected. At 7500 ppm, vaginal patency (VP) and preputial separation (PPS) were delayed in F1, F2, and F3 offspring, associated with reduced body weights. Anogenital distance (AGD) on PND 0 was unaffected for F2 and F3 males and F3 females (F2 female AGD was increased at some doses, not at 7500 ppm, and was considered not biologically or toxicologically relevant). Adult systemic no observed adverse effect level (NOAEL) = 75 ppm (5 mg/kg/day); reproductive and postnatal NOAELs = 750 ppm (50 mg/kg/day). There were no treatment-related effects in the low-dose region (0.001-5 mg/kg/day) on any parameters and no evidence of nonmonotonic dose-response curves across generations for either sex. BPA should not be considered a selective reproductive toxicant, based on the results of this study.     

Adverse effects of diisooctyl phthalate on the male rat reproductive development following prenatal exposure

In a first study, rats were given diisooctyl phthalate (DIOP, CAS 27554-26-3) at 0, 0.1, 0.5, and 1 g/kg/day, by gavage, on gestation days 6–20 (GD). There was a significant increase in resorptions at 1 g/kg/day and a reduction in fetal weights at 0.5 and 1 g/kg/day. Malpositioned testes were observed in fetuses at 1 g/kg/day, and supernumerary lumbar ribs and ossification delay at 0.5 and 1 g/kg/day. In a follow-up study, DIOP administered on GD 12–19 reduced fetal testicular testosterone at 0.1 g/kg/day and above. Finally, postnatal reproductive assessment was conducted in adult male offspring prenatally exposed to DIOP on GD 12–21. Abnormalities of reproductive system (e.g. hypospadias, non scrotal testes, and hypospermatogenesis) were observed in a few adult males at 0.5 g/kg/day, and with a high incidence at 1 g/kg/day. Thus, DIOP displayed an antiandrogenic activity and disrupted the male reproductive development.     

Effects of n-butylparaben on steroidogenesis and spermatogenesis through changed E2 levels in male rat offspring

Parabens are widely used as antibacterial agents, which are concerned recently in the relationship between the use of parabens and reproductive toxicity. So that reassessment of the risk of parabens is needed. In this study, one of parabens, n-butylparaben (n-BP) was orally administered to pregnant Wistar rats (0, 64, 160, 400 and 1000 mg/kg/day) from gestation day (GD) 7 through postnatal day (PND) 21. Reduced anogenital distance (AGD) and delayed preputial separation (PPS) were observed in the male offspring. The weights of the testes were significantly reduced at PND 21–90. The weights of the epididymides were significantly reduced at all monitoring points, except PND 35. Seminal vesicle weights were significantly reduced on PND 21. Serum testosterone (T) was significantly decreased, especially on PND 49. The levels of 17β-estradiol (E₂) showed an increase at each of the tested points except on PND 180. Serum luteinising hormone (LH) and follicle-stimulating hormone (FSH) levels in the n-BP treated groups were lower on PND 21, 35 and 49 but elevated on PND 90 compared to control levels. n-BP reduced epididymal cauda sperm counts and daily sperm production in a dose-dependent manner; this difference was statistically significant at exposure groups of 400 and 1000 mg/kg/day. The present study strongly suggests that exposure to n-BP in utero and during lactation has adverse effects on the reproductive system in male offspring, with a no observed adverse effect level (NOAEL) of 160 mg/kg/day. To our knowledge, this is the first study that reports increased E₂ levels of male rats following n-BP exposure; we suggest that E₂ levels may be considered as biomarkers for some endocrine disrupting chemicals (EDCs).     

Gestational and lactational exposure to ethinyl estradiol, but not bisphenol A, decreases androgen-dependent reproductive organ weights and epididymal sperm abundance in the male long evans hooded rat.

Many chemicals released into the environment are capable of disrupting normal sex steroid balance, including the oral contraceptive ethinyl estradiol (EE) and the plastic monomer bisphenol A (BPA). EE and BPA are reported to impair reproductive organ development in laboratory animals; however, effects of lower doses of these chemicals have been debated. The goal of the current study was to determine whether relatively low oral doses of EE or BPA would alter male reproductive morphology and associated hormone levels of Long Evans hooded rat. Dams were gavaged with corn oil vehicle, EE (0.05-50 mug/kg/day) or BPA (2, 20, and 200 mug/kg/day) during pregnancy through lactation from gestational day 7 to postnatal day (PND) 18. Anogenital distance was measured at PND2 and nipple retention was measured at PND14 in male pups. Male offspring were euthanized beginning at PND150, and sera and organs were collected for analyses. Adult body weight was significantly decreased in males exposed to 50 mug EE/kg/day. Developmental EE exposure reduced androgen-dependent tissue weights in a dose-dependent fashion; for example, seminal vesicle and paired testes weights were reduced with >/= 5 mug EE/kg/day. Epididymal sperm counts were also significantly decreased with 50 mug EE/kg/day. In contrast, treatment with 2, 20, or 200 mug BPA/kg/day or EE at 0.05-1.5 mug/kg/day did not significantly affect any male endpoint in the current study. These results demonstrate that developmental exposure to oral micromolar doses of EE can permanently disrupt the reproductive tract of the male rat.