Structure-activity studies of 2,3,4,4a,5,9b-hexahydroindeno[1,2-c]pyridines as antispermatogenic agents for male contraception.

Analogs of (4aRS,5SR,9bRS)-2-ethyl-2,3,4,4a,5,9b-hexahydro-7-meth yl-5-p- tolyl-1H-indeno[1,2-c]pyridine (Sandoz 20-438, 10a; R1 = ethyl, R2 = R3 = methyl, R4 = H) have been synthesized and tested in mice for their ability to reduce testes weight and disrupt spermatogenesis. The activity was strongly dependent on stereoisomerism and chirality, consistent with a mechanism of action involving interaction with a specific macromolecule. It was affected by changes in the nitrogen substituent and most strikingly by changes in the p-substituent of the 5-aryl ring. A hydrogen, fluorine, hydroxy, or methoxy substituent led to loss of activity, whereas methyl (Sandoz 20-438, 10a), carboxylate (RTI-4587-054, 10k; R1 = ethyl, R2 = methyl, R3 = COOH, R4 = H), ester (RTI-4587-056, 12b; R1 = ethyl, R2 = methyl, R3 = COOMe, R4 = H), formyl (RTI-4587-030, 12i; R1 = ethyl, R2 = methyl, R3 = CHO, R4 = H), or hydroxymethyl (RTI-4587-055, 12g; R1 = ethyl, R2 = methyl, R3 = CH2OH, R4 = H) groups resulted in antispermatogenic compounds. Methyl ester 12b was an effective antifertility agent, without apparent effects on mating, when given orally to male mice at 7-15 mg/kg daily for 35 days. Further evaluation of these compounds as male contraceptive agents and probes for study of spermatogenesis appears warranted.

Response of the pituitary and thyroid to tropic hormones in Sprague-Dawley versus Fischer 344 male rats.

Modulation of endocrine function is frequently a confounding factor in the interpretation of chronic rodent toxicology studies. Of particular interest are agents that cause deviation of thyroid hormone homeostasis and result in thyroid cancer for rodents. An endocrine challenge test (ECT), commonly used to study endocrine organ health in human and veterinary medicine, quantifies the response of the thyroid to tropic hormones. This study compared the response of Fischer (F344) and Sprague-Dawley (SD) rats to a thyrotropin-releasing hormone (TRH) ECT and a thyroid-stimulating hormone (TSH) ECT and characterized the dose-response curve. TSH, thyroxine (T4), triiodothyronine (T3), and prolactin responses were characterized for several doses of TRH over a 4-h time period. Animals were equipped with intra-atrial cannulae and were free moving at all times during blood sampling. Both strains of rats responded to intravenous TRH by releasing TSH into their blood in a dose-responsive fashion. At doses of > or = 100 ng, TSH concentrations were increased by more than 2-fold at 2 min. Concentrations reached a maximum at 15 min for doses of 100 ng/100 g body weight (bw) to 5000 ng/100g bw. The effective dose 50 (ED50) of TRH (that dose causing release of half maximal TSH concentrations) was 61 ng in F344 rats and 78 ng in SD rats. The ED75 was 173 ng and 217 ng/100 g bw, respectively. The response of T4 and T3 after TRH ECT and TSH ECT was highly variable. F344 rats responded with an increase in levels of both hormones, starting at 60 min and continuing through 240 min. In SD rats, the presence of a thyroid hormone response (T4) was present, although that of T3 was not clear. These data provide essential information for design of toxicology studies focused on the effects of toxicants and drugs on the pituitary-thyroid axis.

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.

Comparative effects of quinacrine and erythromycin in adult female rats: a nonsurgical sterilization study.

OBJECTIVE: To compare the efficacies of erythromycin and quinacrine for nonsurgical sterilization in rats. Quinacrine used for nonsurgical sterilization in women is mutagenic, and most clinical regimens have had a higher failure rate than surgical sterilization. DESIGN: This acute mammal study included five groups of rats assigned randomly and evaluated at two times after treatment. ANIMAL(S): Adult female Sprague-Dawley rats. INTERVENTION(S): Five groups of female Sprague-Dawley rats (20 per group) were given 70 or 280 mg/kg of erythromycin lactobionate, 350 mg/kg of quinacrine hydrochloride, or vehicle control administered transcervically. Rats were mated 21 days later. Additional groups (n = 4 per group) were treated and killed 21 days later without mating. MAIN OUTCOME MEASURE(S): Fourteen days after mating, numbers of ovarian corpora lutea, total uterine implants, and embryos were evaluated. For unmated animals, uterine sections were examined for fibrosis and lumen closure. RESULT(S): Neither drug altered numbers of corpora lutea. Erythromycin decreased pregnancy rate and number of implantations (increased preimplantation loss) in a dose-related fashion. Quinacrine increased resorptions. Uterine pathology was more extensive and frequent in erythromycin-treated animals, with extent and severity increasing from 21 to 35+ days. CONCLUSION(S): Erythromycin was more effective than quinacrine in preventing pregnancy.

Influence of photoperiod, ambient temperature and melatonin on testosterone synthesis and release during reproductive maturation in male deer mice.

Four experiments were designed to investigate the influence of photoperiod and other environmental factors on androgen production and reproductive maturation in deer mice. Male prairie deer mice (Peromyscus maniculatus), born in a light/dark cycle of 6L:18D, either remained in this short photoperiod or were switched to a long day regimen of 16L:8D at weaning. In a cross-sectional experiment, the deer mice were killed between 3 and 8 weeks of age for measurement of serum testosterone concentration and reproductive organ weights. In a second experiment, blood was collected from each mouse at weekly intervals between 3 and 9 weeks of age. This repeated measures design was used to reduce the high variability in testosterone values observed in the first experiment. Reproductive organs were weighed at the termination of the experiment. Testosterone concentrations and reproductive organ weights were greater in males reared in the long photoperiod in both experiments. In a third experiment, the animals were housed under five different conditions to test the influence of high ambient temperature and melatonin as well as photoperiod. At 7 weeks of age, they received an injection of hCG or saline. More testosterone was released in deer mice reared in 16L:8D and 27 C than in those reared in short days (6L:18D) or those reared in high ambient temperature (35 C) or those treated with exogenous melatonin. One week later, animals were sacrificed. The single hCG treatment caused significant reversal of the suppression of accessory sex organ weights following melatonin, short days or 35 C temperature. In a fourth experiment, the additive influence of melatonin and 35 C temperature was tested. Animals treated with 35 C or both melatonin and 35 C had lower serum testosterone at 7 weeks of age, released less testosterone after hCG, and had smaller organ weights with or without hCG than long day controls. The influence of melatonin treatment and 35 C temperature appears to be additive for testicular weight and testosterone release after hCG. Thus, the attenuation of reproductive development that accompanied short days, melatonin treatment and high ambient temperature occurred via diminished testosterone secretion, which can be overcome at least in part by gonadotropin treatment.

Reversal of activity profile in analogs of the antiprogestin RU 486: effect of a 16 alpha-substituent on progestational (agonist) activity.

16 alpha-Ethyl-17 beta-acetyl substitution in the D-ring of steroids having an 11 beta-aryl-4,9-dien-3-one structure resulted in compounds with strong progestational activity. These compounds caused endometrial proliferation in the uterus of estrogen-primed rabbits with a potency greater than that of progesterone and had no detectable antiprogestational activity in this model. This is in stark contrast with the marked antiprogestational activity in rabbits, rats and humans reported for most 11 beta-aryl-4,9-diene-3-keto steroids such as RU 486 and its 17 beta-acetyl-17 alpha-acetoxy analog, 17 alpha-acetoxy-11 beta-(4-N,N-dimethylaminophenyl)-19-norpregna-4,9-diene- 3,20-dione. Examination of structure activity relationships in combination with computer aided molecular modelling suggests that a binding interaction of the 16 alpha-ethyl group with the progesterone receptor (PR) or the PR-progestin response element complex may play the major role in this reversal of activity profile.

28-day toxicology test: indenopyridine RTI 4587-056 in male Sprague-Dawley rats.

The potential toxicity of RTI 4587-056, a hexahydroindenopyridine analog of SANDOZ 20-438, was examined in adult male Sprague-Dawley rats. Testicular, intestinal, and erythropoietic histology was assessed after 28 days of gavage treatment at 0, 10, and 100 mg/kg/day. During the first 10 days, dose-related clinical signs included mild to moderate lethargy shortly after dosing, lower consumption of feed and water, and body weight loss or decreased weight gain. Tolerance developed, such that lethargy disappeared and weight gains were equivalent to the control group during the second through fourth weeks. The compound did not affect intestinal epithelium or bone marrow. RTI 4587-056 was a highly effective antispermatogenic agent at both doses causing epididymal hypospermia and testicular atrophy. Based upon the Spermatogenic Index ratings, still lower doses would be effective male contraceptive agents. RTI 4587-056 has potential as a male contraceptive without overt side effects. Further testing is required.

General, reproductive, developmental, and endocrine toxicity of boronated compounds.

Boric acid and inorganic borates are abundant in nature. They are widely used in industrial, agricultural, cosmetic, and numerous smaller applications. These compounds are toxic to all species tested at high doses, but they are not carcinogenic or mutagenic. The major toxicities are reproductive and developmental. Testicular effects occurred at approximately 26 mg boron equivalents/kg body weight (bw)/d (26 mg boron equivalent (BE)/kg bw/d). New data on endocrine toxicity includes altered follicle stimulating hormone and testosterone within 14 d of treatment. Because these hormonal changes may be secondary effects of testicular toxicity, borates are not suspect as endocrine disrupters. The most sensitive of all the endpoints are prenatal growth and morphologic development in the rat; these changes occurred at a dose of 12.9 mg BE/kg bw/d. The no observed adverse effect level for rat fetal development was 9.6 mg/kg BE. Considering the estimated human exposure levels and a safety factor of 30, humans are not at significant risk of reproductive failure due to borates from environmental sources. The margin of exposure is estimated at 72 for males and 129 for females. Thus, the likelihood of human toxicity caused by boric acid and inorganic borates from exposure during normal activities is remote.

Formamide and dimethylformamide: reproductive assessment by continuous breeding in mice.

Reproductive toxicity in Swiss mice, during chronic exposure to formamide (FORM) or dimethylformamide (DMF), was evaluated using the Reproductive Assessment by Continuous Breeding Protocols. FORM administered in drinking water at 0, 100, 350, and 750 ppm (approximately 20 to 200 mg/kg/d) reduced fertility and litter size in F0 animals without generalized toxicity at 750 ppm FORM. Crossover matings suggested that females were the affected sex. After F1 mating, FORM reduced F2 litter size, increased days to litter, reduced relative ovarian weight, and lengthened estrous cycles at 750 ppm. The No-Observed-Adverse-Effect-Level for generalized toxicity was 750 ppm for the F0 and 350 ppm for the F1 generation. Reproductive performance was normal at 350 ppm for both F0 and F1 mice. Chronic exposure to DMF in drinking water at 0, 1000, 4000, and 7000 ppm (approximately 200 to 1300 mg/kg/d) reduced fertility by the first litter at 4000 ppm, reduced body weight in F0 females at 7000 ppm, and increased liver weights at all doses in both sexes. A crossover mating at 7000 ppm identified F0 females as the affected sex. F1 postnatal survival was reduced at > or =4000 ppm DMF. F1 mating reduced F2 litter size and live pup weight at > or =1000 ppm. At necropsy, body weight of F1 males and females was reduced at > or =4000 ppm. DMF-treated pups (both F1 and F2) and F1 adults had cranial and sternebral skeletal malformations. Only DMF caused overt developmental toxicity. A No-Observed-Adverse-Effect-Level for DMF was not established.

Influence of cortisol on prostaglandin synthesis by fetal membranes, placenta, and uterus of pregnant rabbits.

Two experiments were designed to assess the effects of cortisol on prostaglandin formation in amniotic fluid and the prostaglandin-forming cyclooxygenase in 4 gestational tissues of rabbits. Cortisol treatment (12 mg/kg body wt/h) was initiated on Day 21 of pregnancy and continued for a 24-h period. Each experiment included 5 treated and 5 vehicle-injected controls, killed at 48 (Experiment 1) or 62 h (Experiment 2) after initial injection. In both experiments, amniotic fluid was collected; cortisol, prostaglandin F (PGF), and prostaglandin E2 (PGE2) were quantified by radioimmunoassay. Microsomes prepared from amnion, yolk sac splanchnopleure, uterus, and placenta were analyzed for prostaglandin-forming cyclooxygenase activity. In Experiment 2, blood drawn at 12-h intervals was quantified for PGF, PGE2, and progesterone. In cortisol-treated rabbits, plasma progesterone decreased (p less than 0.01) from 7.2 +/- 0.8 ng/ml on Day 21 (pre-treatment) to 1.6 +/- 0.2 ng/ml on Day 23, 48 h after the initiation of cortisol treatment. By 62 h, PGF, PGE2, and cortisol concentrations were all significantly higher (p less than 0.05) in the amniotic fluid of treated animals. However, prostaglandin-forming cyclooxygenase activity had not increased in most fetal or maternal tissues at either 48 or 62 h. Therefore, even though increased prostaglandin production may be responsible for the cortisol-induced abortion, increased cyclooxygenase activity in the fetal membranes, placenta, or uterus probably is not the primary stimulus for the increased prostaglandin synthesis.

Progesterone levels during pregnancy in the greater thick-tailed galago (Galago crassicaudatus).

Serum progesterone concentrations in Galago crassicaudatus were quantified at 3-week intervals throughout the 136-day pregnancy. Progesterone concentrations were significantly elevated over those of nonpregnant controls as early as 6 weeks after conception. Progesterone continued to increase throughout gestation. The progesterone profile in pregnant G. crassicaudatus quantitatively resembles that of chimpanzees and qualitatively resembles that of humans. In two animals that aborted, progesterone concentrations after abortion decreased to values comparable to those seen in nonpregnant animals.

Nitrofurazone: reproductive assessment by continuous breeding in Swiss mice.

Nitrofurazone (NTFZ), a nitrofuran antibiotic, was evaluated for reproductive toxicity in Swiss CD-1 mice using the Reproductive Assessment by Continuous Breeding protocol. Male and female mice were cohabited for 15 weeks and exposed to NTFZ in feed at concentrations of 0, 100, 375, and 750 ppm (14-102 mg/kg/day). Fzero 750-ppm breeding pairs had significantly reduced fertility after 7 days of exposure to NTFZ (17% fertile compared to 98% for control pairs) and were infertile after the second litter. Fzero mid-dose pairs had progressively decreasing fertility (47% by the fifth litter), reduced litter size, and reduced proportion of pups born alive. Crossover breeding of control and high-dose Fzero animals confirmed infertility in high-dose males and reduced litter size and pup weight in high-dose females when compared to the control x control group. At necropsy, there were no effects on body weight, but Fzero males had reduced testis weight at the high dose and reduced epididymal sperm concentration and abnormal sperm morphology at all doses of NTFZ. Increased liver as well as kidney and adrenal weights (combined) were observed at 375 and 750 ppm; hepatic hypertrophy was noted microscopically at 750 ppm. Fzero females had reduced body weight, hepatic hypertrophy, and altered estrous cycles at 750 ppm and reduced ovarian weight at all doses. In the second generation, F1 mice at 375 ppm had reduced postnatal survival and body weight and produced smaller F2 litters compared to control mice. At necropsy, F1 males had reduced testes weight and epididymal sperm concentration, abnormal sperm morphology, hepatic hypertrophy at 375 ppm, and borderline nephropathy at 100 and 375 ppm. F1 females had decreased body, liver, and ovarian weight at 375 ppm and altered estrous cycles at 100 and 375 ppm. Thus, NTFZ at > or = 100 ppm (> or = 14 mg/kg/day) caused adverse reproductive effects in Fzero male and female and F1 female mice in the presence of relatively mild systemic toxicity.

Assessment of polystyrene extract for estrogenic activity in the rat uterotrophic model and an in vitro recombinant receptor reporter gene assay.

The purpose of the study was to determine whether polystyrene used in food-contact applications would elicit an estrogenic response when extracts simulating exaggerated conditions of use were subjected to in vivo and in vitro tests. A sample of polystyrene was subjected to extraction conditions that simulate, or exaggerate, the actual food-contact uses of polystyrene to maximize the amount of low molecular weight polystyrene extractables. The food-simulating solvent and the time and temperature conditions recommended by the Food and Drug Administration (FDA) were selected to maximize the level of extractable components from polystyrene. The extract was examined for its estrogenic response in vivo using the immature rat uterotrophic assay and in vitro using an estrogen receptor (ER)-mediated recombinant receptor reporter gene assay. In vivo, the uterine weights of juvenile female Sprague Dawley rats (10 rats/group) were determined after oral gavage exposure to the extract (two dosage levels: one represents the maximum potential daily human exposure to polystyrene extractables and the other represents one-tenth of the maximum exposure level), vehicle control (sesame oil), or positive control [diethylstilbestrol (DES), at 200 micrograms/kg body weight]. In addition, five treatment groups were dosed by subcutaneous injection of either estradiol (1, 50, and 500 micrograms/kg body weight) or DES (2 and 200 micrograms/kg body weight). Dosing began on postnatal day (pnd) 21 and continued daily through pnd 23. Body weights were collected at study initiation (pnd 21) and at necropsy (pnd 24). Body weights were not different statistically between treatment groups at study initiation or at necropsy. Uterine wet weights and uterine weights relative to body weights were significantly increased (p < 0.05) for estradiol at 50 and 500 micrograms/kg, DES at 2 and 200 micrograms/kg, and DES at 200 micrograms/kg (oral) over vehicle control. The polystyrene extract had no effect on uterine wet weight or uterine weights relative to body weights at either level tested. An in vitro recombinant estrogen receptor/reporter gene assay that involved transiently transfecting MCF-7 human breast cancer cells with the chimeric human ER, Ga14-HEGO, consisting of the yeast Ga14 DNA binding domain linked to the ligand binding domain of the human ER and a Ga14 response element (17mer)-regulated reporter gene (17m5-G-Luc) was employed. Dose-dependent induction of the reporter gene, 17m5-G-Luc, was observed with the positive control, 17 beta-estradiol (E2). Induction of greater than 100-fold was obtained following incubation of transfected MCF-7 cells with 10 nM E2 for 24 hours. No induction of reporter gene activity was observed with the polystyrene extracts dissolved in dimethylsulfoxide (0.01, 0.1 or 0.01 mg/ml) using the same assay conditions. These results indicate that polystyrene extract does not elicit ER-mediated activity using the Ga14-HEGO/17m5-G-Luc recombinant receptor/reporter gene assay. In conclusion, extracts from polystyrene produced no estrogenic response in either the rat uterotrophic assay or the MCF-7 cell assay for estrogen receptor-mediated activity.

Effects of D-ring substituents on antiprogestational (antagonist) and progestational (agonist) activity of 11 beta-aryl steroids.

The discovery of antiprogestational steroids by the Roussel-Uclaf group not only was a major scientific advance but also opened the way to new methods of fertility control and new therapies for such conditions as cancer. RU486, the prototype of the series, is distinguished by a p-(N,N-dimethylaminophenyl) substituent at the 11 beta- position of the steroid framework, a 4,9-dien-3-one system and 17 beta-hydroxy-17 alpha-propynyl substituents. We examined the effect of varying the 17 alpha- substituent in 17 beta-hydroxy compounds analogous to RU486, the effect of introducing a progesterone side chain at C-17, and the effects of further substitution at C-17 alpha and C-16 alpha on the activity of these latter compounds. These studies indicate an important role for D-ring substituents in determining the balance of agonist/antagonist activity in this series. For example, 17 alpha-acetoxy-17 beta-acetyl substitution gave a potent antagonist, whereas 16 alpha-ethyl-17 beta-acetyl substitution resulted in a compound with potent progestational (agonist) activity. The compounds present opportunities for further interesting and useful biological investigations.

Carisoprodol: reproductive assessment by continuous breeding in Swiss mice.

Carisoprodol (CARI), a commonly prescribed neuromuscular relaxant, was evaluated for reproductive toxicity in Swiss CD-1 mice using the Reproductive Assessment by Continuous Breeding (RACB) protocol. Male and female mice were given CARI in corn oil suspension by daily gavage at doses of 0, 300, 750, and 1200 mg/kg body wt/day. Clinical signs of general toxicity in F0 animals included sedation, primarily in the high-dose group during the first week of exposure, and reduced body weight in high-dose females. CARI administration for 14 weeks did not affect the ability of the F0 animals to produce litters. However, decreases in proportion of pups born alive (4%) and absolute (5%) and adjusted live pup weight (7%) were observed at 1200 mg/kg CARI when compared to controls. In a crossover mating trial to determine the affected sex, there were no significant differences in the measured reproductive parameters. CARI at the high dose increased the proportion of time spent in proestrus and estrus, but cycle length was unaffected. At F0 necropsy (Week 27 of treatment), all sperm parameters were normal. Right epididymis and liver weights, relative to body weight, were increased (12 and 23%, respectively) over the control group for high-dose males. A mating trial to determine the fertility and reproductive competence of the F1 generation showed no effect of CARI on indices of mating, pregnancy, or fertility, the proportion of F2 pups born alive, the sex ratio of live F2 pups, live F2 pup weight, or gestation length.(ABSTRACT TRUNCATED AT 250 WORDS)

Reproductive toxicity of boric acid in Swiss (CD-1) mice: assessment using the continuous breeding protocol.

The potential reproductive toxicity of boric acid (BORA) in CD-1 mice (Swiss) was evaluated using the Reproductive Assessment by Continuous Breeding (RACB) Protocol. BORA was administered in the feed for 27 weeks to male and female Swiss (CD-1) mice at concentrations of 0, 1000, 4500, or 9000 ppm. Estimated doses, based on feed consumption and body weight, averaged 152, 636, and 1262 mg/kg body wt during Week 1 for males for 1000, 4500, and 9000 ppm, respectively. During 14 weeks of cohabitation, fertility of F0 mice was partially reduced at 4500 ppm and totally eliminated at 9000 ppm. No litters, dead or alive, were produced by 9000 ppm cohabited pairs. Among the litters born at 4500 ppm, live litter size and body weight were significantly reduced. A crossover mating trial of control and 4500 ppm groups confirmed the male as the affected sex, with fertility rates and the mating index significantly lower in the 4500 male x 0 ppm female group. At necropsy, after 27 weeks of BORA exposure, dose-related changes were present in F0 males for reduced body and reproductive organ weights, increased incidence of abnormal sperm, decreased sperm concentration and motility, and seminiferous tubule degeneration. In the 4500 ppm females, dietary BORA for 27 weeks caused significantly decreased weights of kidney/adrenals and livers; kidney/adrenal weight was also reduced in 4500 ppm males. The last litters of the control and 1000 ppm females, born in the 14-week breeding phase, were reared to 74 days of age and then mated in nonsibling pairs within treatment groups. These F1 mice had normal fertility, but the adjusted mean body weight of F2 pups was decreased. These data establish the reproductive toxicity of BORA in CD-1 mice and demonstrate that the male is the most sensitive sex.

Reproductive effects of 4-vinylcyclohexene in Swiss mice assessed by a continuous breeding protocol.

4-Vinylcyclohexene (VCH), a dimer of 1,3-butadiene, was evaluated for reproductive toxicity in Swiss (CD-1) mice using the continuous breeding protocol (NTP, 1989). VCH in corn oil was administered by gavage at doses of 0, 100, 250, and 500 mg/kg/day to animals that were housed in same sex pairs for 1 week and then cohabited in breeding pairs for 14 weeks. During cohabitation, newborn litters were euthanized immediately after evaluation on postnatal Day (PND) 0. Litters born after Week 15 were reared until PND 21, when all F0 animals and low- and mid-dose F1 weanlings were humanely killed without a necropsy. At PND 74 +/- 10, control and high-dose F1 animals were cohabited within groups for 1 week and necropsied after delivery of the litters. In F0 breeding pairs, VCH did not affect measures of reproductive competence, including initial fertility, litters per pair, live litter size, or the proportion of pups born alive. Pup weight was decreased (4%) in the high-dose group relative to controls. High-dose F0 females exhibited slight general toxicity, manifested as an 8% difference in body weight compared to controls. VCH did not adversely affect preweaning growth or survival in the F1 generation. VCH had no effect on the reproductive competence of the F1 generation. High-dose F1 adult males and females had decreased body weight. At necropsy, increased relative liver weight (males 9% and females 8%) and sperm motility (although not thought to be biologically significant) were observed in the 500 mg/kg VCH group.(ABSTRACT TRUNCATED AT 250 WORDS)

The reproductive and neural toxicities of acrylamide and three analogues in Swiss mice, evaluated using the continuous breeding protocol.

Acrylamide is a known genetic, reproductive, and neural toxicant, although it is not known if one effect is predominant. The toxicities of several structural analogues of acrylamide have been incompletely characterized, and the relative sensitivity of the second generation is not known. The present studies were designed to explore the relationship between neurotoxicity and reproductive toxicity, to further characterize the toxicities of three acrylamide analogues, and to evaluate the relative sensitivity of a second generation to these compounds. For the F0 generation, male and female Swiss CD-1 mice were provided drinking water containing acrylamide (ACR; 3, 10, 30 ppm), N,N'-methylenebisacrylamide (MBA; 10, 30, 60 ppm), N-(hydroxymethyl)acrylamide (HMA; 60, 180, 360 ppm), or methacrylamide (MACR; 24, 80, 240 ppm) during and after a 14-week cohabitation. The last litter was reared and dosed after weaning until mating at 74 +/- 10 days of age with the same level of compound given to the parents Neurotoxicity was assessed at several times in both generations by measuring forelimb and hindlimb grip strength. In the F0 generation, ACR caused an 11% decrease in pup number without measurable neurotoxicity; female fertility was not affected. Although both generations consumed the same amount of ACR, there were larger changes in the fertility-related endpoints in the F1 mice than in the F0's, with no concomitant change in organ weights or sperm parameters. In F0 mice, MBA reduced the number of live pups and their adjusted weight, with no neurotoxicity and no change in F0 female reproduction. MBA caused greater adverse effects in the second generation, concomitant with increased consumption. In the F0 generation, HMA caused the largest decrease in pup number during cohabitation (26%) together with a small effect on grip strength. Female reproduction was not affected. The second generation consumed more HMA and showed slightly greater toxic effects. In both generations, MACR was negative for both neurotoxicity and reproductive toxicity. Dominant-lethal studies showed that the fertility effects for ACR, MBA, and HMA could be explained by a male-mediated increase in postimplantation loss. These studies found that dominant lethality occurred without structural effects on the reproductive system in the presence of only minor effects on grip strength and without detectable neural histopathology. Female reproduction was not significantly affected by these compounds at the doses used. Thus, these data confirm the male as the affected gender and that the reproductive toxicity was greater than motoneuron toxicity when measured as grip strength.

Assessment of the reproductive toxicity of a complex mixture of 25 groundwater contaminants in mice and rats.

The potential reproductive toxicity of a mixture of 25 chemicals (MIX) formulated to simulate contaminated groundwater supplies near hazardous waste dumps was evaluated in CD-1 Swiss mice and Sprague-Dawley rats using the reproductive assessment by continuous breeding protocol. Male and female mice and rats were exposed to MIX in the drinking water at concentrations of 1, 5, and 10% of a technically achievable stock solution. For mice, body weight and feed consumption were not affected by MIX but water consumption was decreased for both the 5 and 10% MIX groups in both F0 and F1 animals. For F0 mice, the number of live pups/litter was decreased at 10% MIX and the number of females/litter was decreased 10 and 17% at the mid and high MIX dose, respectively. Vaginal cytology was normal, as were testis weight and testicular spermatid head count. For F1 mice, fertility was unaffected, but there was a decreased number of female pups/litter (19%) and a decreased adjusted live pup weight at 10% MIX. At necropsy, cauda epididymal sperm concentration and spermatid head count were reduced (20%) in the presence of normal testis, epididymis, prostate, seminal vesicle, liver, and kidney/adrenal weight. Female estrous cyclicity was altered at 5 and 10% MIX with normal kidney/adrenal, uterus, and ovary/oviduct weight. For rats, F0 body weight and feed consumption were not affected by MIX but water consumption was decreased 10, 30, and 40% in the low-, medium-, and high-dose MIX groups, respectively, and 39% in the high-dose MIX F1 animals. Rat fertility was normal but there was a decreased number of male pups/litter (11%) and a decreased live pup weight (6%) at 10% MIX. Male and female (F1) pup weights were decreased on Postnatal Days 0, 4, 7, 14, and 21 (10% MIX) and remained lower through necropsy on Day 120 +/- 10. F1 fertility was normal but F2 pup weights were decreased (10% MIX). At necropsy, F1 (10% MIX) male body weight was decreased 16% and relative kidney, testis, epididymis, and prostate weights were increased in the presence of normal sperm concentration percentage motile sperm and percentage abnormal sperm. Estrous cyclicity was normal as were kidney/adrenal and ovary weight while female liver weight was reduced 14%. In summary, a "cocktail" of 25 chemicals commonly found in contaminated groundwater at or near hazardous waste sites was administered in drinking water at doses which resulted in severely decreased water consumption in both mice and rats.(ABSTRACT TRUNCATED AT 400 WORDS)