Twenty-week exposures to the drinking water disinfection by-product dibromoacetic acid: reproductive cyclicity and steroid concentrations in the female Sprague-Dawley rat

Elevated gavage exposures to the drinking water disinfection by-product dibromoacetic acid (DBA) have been found to disrupt estrous cyclicity in the rat and induce increases in estradiol concentrations in both cycling (day of estrus) and ovariectomized/estradiol-implanted females. The present study was designed to investigate both effects in Sprague-Dawley rats following an extended 20-week treatment with lower dosages of DBA administered in the drinking water (calculated mean intake concentrations of 5, 16, and 33 mg/kg/d). No treatment-related effects on cyclicity were present, although elevations in serum estradiol on the day of vaginal estrus were noted in regularly cycling rats when assessed at the 3rd and 11th weeks of exposure. By the 19th week, this effect was no longer present in cycling animals, but its absence was attributable to a marked increase in control estradiol concentrations, which may be associated with endocrine alterations that precede a disruption in estrous cyclicity in middle-aged females. In the 20th week, diestrous estrone levels were elevated at all dosages without effects on serum androstenedione or progesterone. Uterine and pituitary weights were unchanged at this time, although there were modest increases in liver weights at the two highest dosages. A small number of rats in persistent estrus (PE) did show a general increase in pituitary weight associated with DBA exposure, possibly reflecting an added layering of treatment on the PE-associated rise in estradiol normally seen in these females. The results indicate that increases in circulating estradiol from drinking water exposures to DBA were not linked to a premature disruption of estrous cyclicity in this moderately estrogen-sensitive rat strain.     

Reproductive effects of nonylphenol in rats after gavage administration: a two-generation study

The potential reproductive toxicity of nonylphenol (NP) was assessed in a two-generation reproductive toxicity study. Groups of 25 male and female Crj:CD (SD) IGS rats were given NP by gavage at levels of 2, 10, or 50 mg/kg, and 25 males and females were given corn oil as controls. No adverse changes in clinical signs were observed in any rats throughout the study. Significant increases in the liver, kidney and pituitary gland weights in males, and decreases in thymus weight in males and in ovary weight in females were observed in the 50 mg/kg group. NP did not affect sperm characteristics or the estrous cycle at any dose administered. A significant increase in the TSH level was observed in males in the 50 mg/kg group. No adverse effects of NP on reproduction were found. At necropsy, no treatment-related alterations were observed in any organs including the reproductive tissues in any group. Histopathologic changes were found in the liver of male and female rats and kidneys of males in the 50 mg/kg group. The viability of offspring from postnatal day 0 to 4 in the 50 mg/kg group was reduced as compared with that in the controls, although growth was not affected by NP administration. On postnatal day 22, an increase in the serum FSH level and decrease in T(3) level for males, and decreases in LH and TSH levels and an increase in T(3) levels for females were observed in the 50 mg/kg group. NP did not affect the timing of preputial separation, while vaginal opening was accelerated in the 50 mg/kg group. No adverse changes were found in behavior or learning in the offspring of NP-treated groups. There were no treatment-related changes in any reproductive parameter, including estrous cycle, mating, fertility, delivery, and lactation, except for significant decreases in the numbers of implantation sites and live pups, and a significant decrease in ovary weight in the 50 mg/kg group. Kidney and liver weight were increased in males in the 50 mg/kg group. Histopathologic examination revealed changes in the liver of males and females of the 50 mg/kg group. No treatment-related changes were observed in the sperm characteristics. Hormone data should be interpreted cautiously until the findings are repeated and confirmed by further studies. These results of NP suggested that the no observed adverse effect level (NOAEL) on reproductive capacity is 50 mg/kg/day or greater in parent animals, and 10 mg/kg/day in the next generation under the present experimental condition.     

A repeated 28-day oral dose toxicity study of methoxychlor in rats, based on the 'Enhanced OECD Test Guideline 407' for screening endocrine-disrupting chemicals

In association with the international validation project to establish an OECD Enhanced Test Guideline 407, we performed a 28-day repeated-dose toxicity study of methoxychlor, a chlorinated hydrocarbon pesticide with pro-estrogenic and anti-androgenic activities. Attention was paid to the sensitivity of certain additional parameters for detecting endocrine related effects of endocrine disrupting chemicals based on the existing TG 407. Seven-week-old Crj:CD(SD)IGS rats were allocated to one of four groups, each consisting often males and ten females, and methoxychlor was administered once daily by gavage at doses of 0 (control), 20, 100 or 500 mg/kg body weight per day. Male rats were killed on the day after the 28th administration. Female rats were killed on the day of the diestrus stage during 4 days after the 28th administration. Male rats receiving methoxychlor showed mainly atrophy of mammary acinus in the 20 mg/ kg and higher groups, together with decreases in prostate and seminal vesicle weights, and atrophy of epididymis, prostate, seminal vesicle and coagulating gland in the 100 and 500 mg/kg groups. In addition, decrease in serum testosterone level, increase in follicle-stimulating hormone level, decrease in testis and epididymis weights, atrophy of semiferous tubules and Leydig cells, decrease in the number of sperm in the caudal epididymis and their motility were observed in the 500 mg/kg group. Female rats receiving methoxychlor showed mainly abnormal estrous cycles, decrease in serum luteinizing hormone level, decrease in ovary weight, proliferation of mammary acinus, atrophy of ovary due to decrease in follicles and corpus luteum in histopathology, hypertrophy of endometrial epithelium of uterus and vagina epithelium in the 100 and 500 mg/kg groups. Among the parameters tested in the present experimental system, effects of methoxychlor on endocrine-related organs were detected with regard to serum hormone, organ weights, histopathological examination in both sexes, estrus cycle in females and sperm examination in males. Based on these results, a no-observed-adverse-effect level (NOAEL) in the present study was estimated to be below 20 mg/kg per day. In particular, the adverse effects were effectively detected in organ weights of accessory sex organs and histopathological examination.     

Perinatal exposure to low doses of tributyltin chloride advances puberty and affects patterns of estrous cyclicity in female mice

Tributyltin (TBT), a proven endocrine‐disrupting chemical, is well known to induce imposex in female gastropods. Herein we demonstrate the effects of low doses of tributyltin chloride (TBTCl) on the female offspring of KM mice. Pregnant mice were administered by gavage with 0, 1, 10, or 100 μg TBTCl/kg body weight/day from day 6 of pregnancy through the period of lactation. TBTCl dramatically advanced the age of onset of vaginal opening (VO) and first vaginal estrus, and reduced body weights at VO and first estrus. Furthermore, perinatal treatment with TBTCl significantly reduced the number of days between VO and first estrus. In addition, female offspring from dams exposed to 10 and 100 μg kg^?1 TBTCl exhibited altered patterns of estrous cyclicity in adulthood. In conclusion, perinatal exposure to low doses TBTCl result in early puberty and impaired estrous cyclicity in female mice, which suggest that TBTCl might act as an estrogen agonist or/and a disruptor on hypothalamic–pituitary function in the present study. © 2012 Wiley Periodicals, Inc. Environ Toxicol, 2012.     

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.     

Relationship between acrylamide reproductive and neurotoxicity in male rats

To determine whether there is a relationship between the reproductive and neurotoxic effects of acrylamide monomer (AM), the first week of the study design of Sublet et al. ?14 was duplicated: Long-Evans male rats were gavaged with AM in water, 25/group, at 0, 5, 15, 30, 45, or 60 mg/kg/day for 5 days (days 1 through 5). On Day 8, males were paired overnight with untreated virgin females (1 : 1) in proestrus/estrus. On day 9, males were evaluated for forelimb and hindlimb grip strength. Five males/group were perfusion fixed, 20/group were used for andrologic assessment, and all were necropsied. Perfusion-fixed sciatic nerves were examined histologically. Sperm-positive females were examined for preimplantation and postimplantation loss at midpregnancy. At 15 to 60 mg/kg/day, males exhibited significantly reduced weight gain, reduced mating, fertility, and pregnancy indices by trend analysis (significant at 60 mg/kg/d by pairwise comparison), and increased postimplantation loss and dominant lethal factor, F(L)%, at 45 and 60 mg/kg/day. At 60 mg/kg/day, the sperm beat cross frequency was increased, with no significant effects on epididymal sperm motility or concentration, and hindlimb grip strength was decreased, with no pathologic lesions in sciatic nerves. Therefore, epididymal sperm, mating, and neurotoxic effects were observed at AM doses that also resulted in increased postimplantation loss, possibly by different mechanisms.     

The development of a protocol to assess reproductive effects of toxicants in the rat

The determination that a chemical poses a reproductive risk to man typically relies upon fertility studies using rodents. However, fertility in rodents is often difficult to disrupt and more sensitive indicators of reproductive function should be included in the risk assessment process. The present discussion compares the sensitivity of fertility to other endpoints following exposure to known reproductive toxicants. In our studies rats were dosed from weaning through puberty, gestation, and lactation. The reproductive function of the male, the female, and the offspring was assessed. The effects of methoxychlor, carbendazim (MBC), dibutyl phthalate (DBP), and lindane are discussed and compared to fertility. For each compound a ratio (SR = sensitivity ratio) of the lowest effect level (LEL) for infertility or reduced fecundity to the LEL for the most sensitive physiologic endpoint was calculated. The SR should be large when a compound produces effects over a wide range of doses, but should equal unity when the dose-response curve is very steep. For methoxychlor, which blocked implantation, pubertal landmarks and estrous cyclicity provided rapid and sensitive indicators of the subsequent reproductive failure. The SR = 8 (100/12) for methoxychlor using data from females. In contrast, DBP and MBC directed altered testicular function, and for these compounds, sperm and testicular measures provided sensitive indicators of toxicity. The SR for MBC was 2 (100/50), while DBP had a SR of 1 (500/500). In the lindane study, fertility was not reduced but most of the pups (F1) died shortly after birth. The SR for lindane is equal to 0.5 (10/20). At 20 mg/kg the treated females were larger and their estrous cycles were erratic. The data from these studies indicate that no single endpoint will consistently be the most sensitive indicator of reproductive toxicity. Studies must include a number of well validated endpoints that provide a comprehensive assessment of the entire reproductive system of the male and female.     

The effects of atrazine on female wistar rats: an evaluation of the protocol for assessing pubertal development and thyroid function.

The effects of atrazine (ATR), a chlorotriazine herbicide, on the onset of puberty were evaluated in Wistar rats. Female rats were dosed by oral gavage from postnatal day(s) (PND) 22 through PND 41 with 0, 12.5, 25, 50, 100, or 200 mg ATR/kg. Vaginal opening (VO) was significantly delayed 3.4, 4.5, or greater than 6.8 days by 50, 100, and 200 mg/kg, respectively. VO had not occurred in 4 of 15 females in the 200 mg/kg group by the time of necropsies (PND 41). Body weight (bw) at necropsy was reduced in the 200 mg/kg group by 11.6%, but was not different from the control (0) in the 50 and 100 mg/kg groups. To examine the influence of reduced bw on pubertal development, a group of pair-fed controls was included whose daily food intake was dependent upon the amount consumed by their counterpart in the 200 mg/kg group. Although necropsy bw was reduced to the same extent as the ATR females, VO in the pair-fed controls was not significantly delayed. Adrenal, kidney, pituitary, ovary, and uterine weights were reduced by 200 mg/kg ATR. Serum T(3), T(4), and TSH were unaltered by ATR, which was consistent with no histopathologic/morphologic changes in the thyroid. Estrous cyclicity was monitored in a second group of females from VO to PND 149. The number of females displaying regular 4- or 5-day estrous cycles during the first 15-day interval after VO was lower in the 100 and 200 mg/kg ATR and pair-fed controls. Irregular cycles were characterized by extended periods of diestrus. By the end of the second 15-day interval (PND 57-71), no effects on estrous cyclicity were observed. These data show that ATR can delay the onset of puberty and alter estrous cyclicity in the female Wistar rat ( NOAEL of 25 mg/kg). Reduced food consumption and bw did not account for the delay in VO, because this effect was not observed in the pair-fed controls. In addition, the effect on estrous cyclicity was observed in the 100 mg/kg ATR group where no significant reduction in bw was observed.     

Reproductive and developmental toxicity screening test of basic rubber accelerator, 1,3-di-o-tolylguanidine, in rats

Twelve male and female rats per group were exposed to the rubber accelerator 1,3-di-o-tolylguanidine (DTG) by gavage at 0, 8, 20 or 50 mg/kg bw/day. Males were dosed for a total of 49 days beginning 14 days before mating. Females were dosed for a total of 40-49 days beginning 14 days before mating to day 3 of lactation throughout the mating and gestation period. At 50 mg/kg bw/day, deaths were observed in two males and three females. Lowered body weight gain and food consumption were noted in males at 50 mg/kg bw/day and females at 20 and 50 mg/kg bw/day. Mydriasis, decreased locomotor activity, bradypnea, prone position, tremor and/or salivation were observed in males and females at 20 and 50 mg/kg bw/day. No effects of DTG were found on the estrous cyclicity, precoital interval, copulation, fertility and gestational indices, numbers of corpora lutea and implantations, or gestation length. A significant decrease in the number, body weight and viability of offspring and increase in the incidence of fetuses with external malformations were found at 50 mg/kg bw/day. Oligodactyly, anal atresia and tail anomalies were observed. These data suggest that DTG may be teratogenic. The NOAELs of DTG for general and developmental toxicity in rats are 8 and 20 mg/kg bw/day, respectively.     

Persistent vaginal estrus and serum hormones after chlordecone (Kepone) treatment of adult female rats

The effects of chlordecone on vaginal estrus and neuroendocrine responses were examined in adult ovariectomized and intact females. Persistent vaginal estrus was seen in females given 50 mg/kg or more of chlordecone. The development of vaginal estrus was similar to that seen in ovariectomized females after treatment with estrogen. Since chlordecone is known to have estrogen-like effects on the reproductive system, the persistent vaginal estrus probably results from this estrogen-like action and chlordecone's long half-life in the organism. Neuroendocrine effects of chlordecone also resembled, to some degree, estrogen's effects on pituitary secretions. Chlordecone increased serum prolactin and decreased serum luteinizing hormone (LH) in ovariectomized females 30 to 36 hr after a single exposure to 50 mg/kg of the pesticide. Basal LH levels were not altered in intact females, but the proestrous LH surge was suppressed by 36 hr after treatment. Both basal and proestrous levels of prolactin were suppressed. Unlike the effects of estrogen, serum follicle stimulating hormone was not altered by chlordecone. These results indicate an effect on the hypothalamic pituitary axis by chlordecone treatment and offer a possible explanation for the reduced fertility seen in adult females after chlordecone exposure. However, blockage of the proestrous LH surge was not obligatory for the appearance of vaginal estrus. Although chlordecone produced peripheral changes in the vaginal smear pattern as well as neuroendocrine alterations, the peripheral changes were not always indicative of the neuroendocrine events.     

Pre-pubertal exposure to ibuprofen impairs sperm parameters in male adult rats and compromises the next generation

ABSTRACT

Ibuprofen is one of the most commonly prescribed anti-inflammatory drugs in pediatric practice. This drug inhibits the cyclooxygenase enzyme, reducing the production of prostaglandin, an important mediator on male reproductive function. We examined if pre-pubertal treatment with ibuprofen in male rats can affect the reproductive parameters of these animals in adult life and on their descendants. Male rats (23 days old) received ibuprofen (0; 2.4; 7.2 or 14.3 mg/kg/day), per gavage, from postnatal day (PND) 23 to 53. At sexual maturity, treated males were placed with untreated females for obtaining the next generation (F1). The highest dose of ibuprofen interfered in sexual behavior and reduced the fertility potential of these animals in adulthood. Additionally, the ibuprofen treatment altered the sperm quantity and quality, as evidenced by a decrease in sperm motility and in the daily sperm production in the testis. Testosterone levels were also reduced by pre-pubertal treatment. The paternal treatment with this drug also influenced the reproductive outcomes of progeny. The male offspring from males treated exhibited acceleration in sperm transit time in the epididymis and the number and volume of Leydig cell nuclei were decreased, while the estrous cyclicity was displayed and the fertility potential reduced in the female offspring. The pre-pubertal ibuprofen-treatment caused negative reproductive impacts in adulthood, compromising sperm quality and quantity, as well as interfered in the reproductive outcomes of the next generation.     

Assessment of reproductive and fertility effects of amitraz pesticide in male mice

Forty adult male Swiss mice were exposed to tap water containing 0, 40, 80, or 160 ppm amitraz for 12 weeks. Based on fluid consumption the mice received an average of 0, 5.42+/-0.47, 10.56+/-0.97, and 20.39+/-2.17 mg/kg/day amitraz, respectively. The average body weights gains and fluid consumption were significantly decreased in males exposed to amitraz pesticide. Fertility was significantly reduced in male mice ingesting 10.56+/-0.97 or 20.39+/-2.17 mg/kg/day amitraz in that the number of females impregnated by them was significantly reduced. The number of viable fetuses was significantly reduced in females mated with males that ingested 10.56+/-0.97 or 20.39+/-2.17 mg/kg/day amitraz. A significant increase in the total number of resorptions and the number of females with resorptions was observed in females impregnated with the exposed males. Absolute testis weight was significantly decreased at 10.56+/-0.97 mg/kg concentration. The weight of the epididymis was decreased in test males ingested 20.39+/-2.17 mg/kg amitraz. The seminal vesicles weights were significantly increased in male mice ingested 10.56+/-0.97 or 20.39+/-2.17 mg/kg/day amitraz. Similarly, the preputial gland weights were increased in males that ingested 5.42+/-0.47 or 10.56+/-0.97 mg/kg and decreased in males ingested 20.39+/-2.17 mg/kg amitraz. Testicular sperm counts and daily sperm production were significantly decreased in males that ingested 10.56+/-0.97 or 20.39+/-2.17 mg/kg/day amitraz. Epididymal sperm counts were significantly decreased in exposed male's at 10.56+/-0.97 or 20.39+/-2.17 mg/kg amitraz. These results strongly suggest that exposure to amitraz pesticide have an adverse effect on the fertility and reproductive system of male mice.     

Effect of butyl benzyl phthalate in Sprague-Dawley rats after gavage administration: a two-generation reproductive study

Butyl benzyl phthalate (BBP), a plasticizer, has been shown in in vitro studies to be weakly estrogenic, and in in vivo studies to possess testicular toxicity and teratogenicity, but few experimental data on BBP multigeneration effects on reproduction in mammals are available. The present two-generation reproductive study was conducted in male and female Sprague-Dawley rats using oral doses of 0, 20, 100, and 500 mg/kg/day BBP. Endpoints were chosen in order to evaluate both subchronic and reproductive toxicity. In the parent animals (F₀), a decrease in body weight gain was observed in males in the 500 mg/kg/day group, although no significant decrease in food consumption was found. No dose-related changes were observed in estrous cyclicity, fertility, or lactation. A dose-dependent increase in kidney weight in rats of both sexes, an increase in liver weight in males, and a decrease in the weight of the ovaries in females were observed. No macroscopic or microscopic changes were found in the reproductive system of males or females. Oral administration of BBP caused a decrease in the serum concentration of testosterone, and an increase in FSH. In the next generation (F₁), the body weight of male and female offspring at birth in the 100 and 500 mg/kg groups was significantly decreased, and the body weight in the 500 mg/kg group was lower throughout the study, while viability was not affected. Anogenital distance (AGD) at birth was decreased in male pups and was increased in female pups of the 500 mg/kg/day group. Preputial separation for male offspring in the 500 mg/kg/day group was delayed, while vaginal opening for female offspring in this group was not affected. BBP did not affect reproductive ability, including delivery and lactation, at any dose whereas macroscopic and microscopic changes of the testis, and decreased serum concentrations of testosterone were observed in male offspring of the 500 mg/kg/day group after puberty. From these data, it would appear that 20 mg/kg BBP is a no observed adverse effect level (NOAEL) for reproductive effects on parent animals and the next generation.     

Estrogenic activity of octylphenol, nonylphenol, bisphenol A and methoxychlor in rats.

Considerable attention has recently been focused on environmental chemicals that disrupt the reproductive system by altering steroid receptor function. Although numerous in vitro and in vivo methods have been shown to be useful approaches for identifying chemicals that can disrupt reproduction through a direct interaction with the estrogen receptor, it is imperative that the protocols selected be capable of detecting chemicals with a broad range of estrogenic activity. Here we evaluate the reliability of the 3-day uterotrophic assay for detecting chemicals with strong or weak estrogenic activity in both prepubertal and ovariectomized adult Long Evans rats. These data were compared to additional measures of estrogenic activity, which included the age of vaginal opening, the induction of cornified vaginal epithelial cells in ovariectomized adult rats, and estrous cyclicity in intact adult rats. Test chemicals selected for these studies included 17-beta-estradiol, ethynyl estradiol, methoxychlor, 4-tert-octylphenol, 4-nonylphenol and bisphenol A. Data from in vitro receptor binding assays compared the ability of the test chemicals to compete with [3H]-estradiol or [3H]-promegestone for binding to estrogen or progesterone receptors. As expected, the binding affinities for the estrogen receptor ranged from high to low, as reflected by Ki concentrations of 0.4 nM for 17-beta-estradiol and ethynyl estradiol, and 0.05-65 microM for 4-tert-octyphenol, 4-nonylphenol, and methoxychlor. Although none of the test chemicals demonstrated a high affinity for binding to the progesterone receptor, 4-tert-octylphenol and 4-nonylphenol exhibited a weak affinity, with Ki concentrations ranging from 1.2 to 3.8 microM. In vivo studies indicated that the 3-day uterotrophic assay in prepubertal rats was the best method for detecting estrogenic activity when compared with all other end points, based upon the dose-response data for ethynyl estradiol (0.01-0.1 mg/kg), 4-tert-octylphenol (50-200 mg/kg, oral), and 4-nonylphenol (25-100 mg/kg, oral). Although oral doses of ethynyl estradiol (0.01 mg/kg) and 4-nonylphenol (50 mg/kg) induced a significant increase in uterine weight in the prepubertal rats, these doses were ineffective for stimulating a similar response in ovariectomized adult rats. The age of vaginal opening was advanced following oral exposure from postnatal days 21-35 to ethynyl estradiol (0.01 mg/kg), methoxychlor (50 mg/kg), 4-tert-octylphenol (200 mg/kg), and 4-nonylphenol (50 mg/kg). Although bisphenol A (200 mg/kg, oral) induced a significant uterotrophic response within 3 days in prepubertal rats, doses up to 400 mg/kg failed to advance the age of vaginal opening. Monitoring changes in the vaginal epithelium of ovariectomized adult rats was the least effective method for detecting estrogenic activity for 4-tert-octylphenol and bisphenol A. The number of 4-5 day estrous cycles was reduced during a 25-day exposure to ethynyl estradiol (0.01 mg/kg), methoxychlor (50 mg/ kg), 4-tert-octylphenol (200 mg/kg), 4-nonylphenol (100 mg/kg), and bisphenol A (100 mg/kg) by oral gavage. Although long periods of extended diestrus (7-14 days) were generally correlated with exposure to ethynyl estradiol and 4-tert-octylphenol, the cycling patterns following exposure to methoxychlor, 4-nonylphenol and bisphenol A were not as clearly defined, with shorter periods of extended diestrus (4-7 days) and/or estrus (3-5 days) intermittently observed throughout the exposure period. Together these data provide a comparison of the 3-day uterotrophic assay with alternative measures of estrogenic activity for a group of test chemicals with a broad range of affinities for the estrogen receptor. These data can be useful during the assessment and validation of methods for screening environmental chemicals for endocrine disrupting activity.     

Gestational exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) severely alters reproductive function of female hamster offspring.

Low doses of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), administered as a single dose to the dam during gestation, alter development of the fetal rodent reproductive system. In male rat and hamster offspring, dosing with TCDD during gestation reduces epididymal and ejaculated sperm counts and delays puberty. In female rats, in utero TCDD-exposure results in reduced ovarian weight and fecundity, and induces cleft phallus and a persistent thread of tissue across the vaginal orifice. Here, we demonstrate that 2-microgram TCDD/kg, administered as a single oral dose prior to sexual differentiation, alters reproductive function in female hamster offspring, a species relatively resistant to the lethal effects of TCDD. In the current study, pregnant hamsters (P0 generation) were dosed orally with vehicle (corn oil) or 2 micrograms TCDD/kg on gestational day (GD) 11.5. P0 maternal viability, body weight, fertility, and F1 litter size did not differ between control and treated groups. In the F1 generation, body weights were permanently reduced by about 30%, vaginal opening was delayed (p < 0.0001), and vaginal estrous cycles were altered by TCDD treatment. In contrast, most treated female offspring displayed regular 4-day behavioral estrous cycles, indicating that in utero TCDD treatment did not markedly disrupt hypothalamic-pituitary-gonadal hormonal cyclicity. Although both control and TCDD-treated F1 females mated successfully with a control male (estrous cyclicity was abolished by mating), 20% of the F1 treated females did not become not pregnant (no implants). In addition, 38% of pregnant F1 females from the TCDD group died near-term, and the numbers of implants in pregnant animals (treated 5.1 versus 11.3) and pups born live (2.7 treated vs. 8.7 control) were reduced by TCDD-treatment. In the F2, survival through weaning was drastically reduced (15% treated vs. 78% for control) by TCDD treatment of P0 dams. F1 female hamster offspring exposed in utero to TCDD displayed external urogenital malformations, with most females having complete clefting of the phallus, an effect previously reported in the rat. Unlike rats exposed to TCDD (0.2-1.0 microgram/kg) on GD 15 or GD 8, hamster offspring did not display vaginal threads. These results demonstrate that in utero administration of TCDD adversely affects growth, reproductive function, and anatomy in female hamster offspring given a dosage level nearly four orders of magnitude below the dosage level toxic to the adult animal. Adverse effects of TCDD persisted through two generations (F1 and F2), even though the F1 was only indirectly exposed during gestation and lactation.     

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.     

Vaginal cyclicity, sexual receptivity, and eating behavior of the female rat following treatment with chlordecone.

The effects of 25, 50, or 75 mg/kg chlordecone on vaginal and behavioral estrus were examined following treatment of intact rats during estrus, diestrus 1, or diestrus 2. Chlordecone accelerated vaginal estrus, but sexual behavior was eliminated, delayed, or reduced. Chlordecone treatment led to the presence of vaginal estrus within 2 days, but reduced or eliminated sexual behavior on the evening of predicted proestrus. Of the females that received chlordecone, 20% to 50% showed some behavior on the day after the evening of predicted proestrus and 20% to 35% never showed behavior during the 8-day observation period. Although the lordosis to mount ratio was still reduced, the occurrence of behavior a day late suggested that the pesticide had delayed behavioral estrus. Chlordecone also rapidly suppressed food intake and led to a significant decline in body weight; these nutritional factors could have contributed to the disrupted estrous cycle. Some support for this possibility was derived from a reduced sexual receptivity on the evening of proestrus when the caloric intake of untreated female rats was matched to that of the chlordecone treated animals. However, the effects of caloric reduction on proestrous lordosis behavior were less robust than seen following chlordecone. Chlordecone treatment on diestrus 2 reduced the number of progesterone receptors in uterine tissue of females on the predicted day of proestrus. This suggested that the tissue sensitivity to circulating levels of progesterone would be reduced within 2 days after chlordecone treatment.(ABSTRACT TRUNCATED AT 250 WORDS)     

The effect of methoxychlor on the epididymal antioxidant system of adult rats

Methoxychlor is widely used as a pesticide in many countries and has been shown to induce reproductive abnormalities in male rats, causing reduced fertility. The mechanism of action of methoxychlor on the male reproductive system is not clear. In the present study we investigated whether administration of methoxychlor induces oxidative stress in the epididymis and epididymal sperm of adult rats. Methoxychlor (50, 100, or 200 mg/kg body weight/day) was administered orally for 1, 4, or 7 days. The animals were killed using anesthetic ether 24 h after of the last treatment. Epididymal sperm were collected by cutting the epididymis into small pieces in Ham's F-12 medium at 35 degrees C. The body weight and weights of the testis, liver, and kidney did not show any significant changes in the methoxychlor-treated rats. The weight of the epididymis, seminal vesicles, and ventral prostate as well as epididymal sperm counts decreased after 50, 100, or 200 mg/kg/day for 7 days but remained unchanged after shorter courses of treatment. Epididymal sperm motility was decreased in a dose-dependent manner in the animals treated with methoxychlor for 4 or 7 days. The activities of the antioxidant enzymes superoxide dismutase, catalase, glutathione reductase, and glutathione peroxidase were decreased while the levels of hydrogen peroxide and lipid peroxidation were increased in the epididymal sperm as well as in the caput, corpus, and cauda epididymis after 4 or 7 days of treatment. The activities of superoxide dismutase decreased while the levels of lipid peroxidation increased in the liver but not in the kidney in all groups. Co-administration of the antioxidant vitamin E (20 mg/kg body weight/ day) to the 200 mg/kg/d methoxychlor-treated rats for 7 days prevented significant changes in the antioxidant systems in the epididymis and epididymal sperm and prevented alterations in sperm counts and motility. The results indicated that methoxychlor induces oxidative stress in the epididymis and epididymal sperm by decreasing antioxidant enzymes, possibly by inducing reactive oxygen species. In conclusion the adverse effect of methoxychlor on the male reproduction could be due to induction of oxidative stress.     

Octyl methoxycinnamate: two generation reproduction toxicity in Wistar rats by dietary administration.

Wistar rats continuously received octyl methoxycinnamate (OMC) in the diet through two successive generations at nominal doses of 0, 150, 450 or 1000 mg/kg bw/day. OMC had no adverse effects on estrous cycles, mating behavior, conception, parturition, lactation and weaning, sperm and follicle parameters, macropathology and histopathology of the sexual organs. 1000 mg/kg bw/day reduced parental food consumption and body weight (-14% to -16% in males, -4% to -5% females), increased liver weight, produced hepatic cytoplasmic eosinophilia and erosion/ulceration of glandular stomach mucosa. and led to a slightly decreased implantation rate in the top dose F0 and F1 dams. The high dose F1 and F2 pups had reduced lactation weight gain and organ weights and delayed sexual maturation landmarks. There was no evidence of a selective influence of the test compound on pups' sexual landmarks. The NOAEL (no observed adverse effect level) is 450 mg/kg bw/day for fertility and reproductive performance, for systemic parental and developmental toxicity.     

Reproductive effects in male and female rats of neonatal exposure to genistein

Sprague-Dawley rats were administered genistein orally at doses of 12.5, 25, 50, or 100 mg/kg on postnatal days 1 through 5 to examine its effects on reproductive function after puberty. In addition, preputial separation and vaginal opening as endpoints of sexual maturation, estrous cycling, sperm count, serum testosterone concentration, and histopathologic changes of reproductive organs of male and female rats were examined. Body weights of male and female rats exposed to genistein at any dose level examined were lower than those of controls. Timing of preputial separation in males and timing of vaginal opening were not affected by genistein treatment. The number of females showing estrous cycle irregularities was increased by genistein treatment. The fertility of female rats exposed neonatally to genistein at 100 mg/kg was disrupted, while neonatal exposure to genistein did not affect male fertility. Neither sperm counts nor serum testosterone concentration were changed by neonatal exposure to genistein. Female rats exposed neonatally to genistein at 100 mg/kg showed histopathologic changes in the ovaries and uterus, while male rats showed no histopathologic alterations in the gonads. The results of this study indicate that early neonatal exposure to genistein caused dysfunction of postpubertal reproductive performance as well as abnormal development of gonads in female but not in male rats.