Two-generation reproduction and cross-foster studies of perfluorooctanesulfonate (PFOS) in rats

Perfluorooctanesulfonate (PFOS) is a persistent acid found widely distributed in wildlife and humans. To understand the potential reproductive and developmental effects of PFOS, a two-generation reproduction study was conducted in rats. Male and female rats were dosed via oral gavage at dose levels of 0, 0.1, 0.4, 1.6, and 3.2 mg/(kg day) for 6 weeks prior to mating, during mating, and, for females, through gestation and lactation, across two generations. Due to substantial F1 neonatal toxicity observed in the 1.6 and 3.2 mg/(kg day) groups, continuation into the second generation was limited to F1 pups from the 0, 0.1, and 0.4 mg/(kg day) groups. No adverse effects were observed in F0 females or their fetuses upon caesarean sectioning at gestation day 10. Statistically significant reductions in body-weight gain and feed consumption were observed in F0 generation males and females at dose levels of 0.4 mg/(kg day) and higher, but not in F1 adults. PFOS did not affect reproductive performance (mating, estrous cycling, and fertility); however, reproductive outcome, as demonstrated by decreased length of gestation, number of implantation sites, and increased numbers of dams with stillborn pups or with all pups dying on lactation days 1-4, was affected at 3.2 mg/(kg day) in F0 dams. These effects were not observed in F1 dams at the highest dose tested, 0.4 mg/(kg day). Neonatal toxicity in F1 pups, as demonstrated by reduced survival and body-weight gain through the end of lactation, occurred at a maternal dose of 1.6 mg/(kg day) and higher while not at dose levels of 0.1 or 0.4 mg/(kg day) or in F2 pups at the 0.1 or 0.4 mg/(kg day) dose levels tested. In addition to these adverse effects, slight yet statistically significant developmental delays occurred at 0.4 (eye opening) and 1.6 mg/(kg day) (eye opening, air righting, surface righting, and pinna unfolding) in F1 pups. Based on these data, the NOAELs were as follows: reproductive function: F0> or =3.2 and F1> or =0.4 mg/(kg day); reproductive outcome: F0=1.6 and F1> or =0.4 mg/(kg day); overall parental effects: F0=0.1 and F1> or =0.4 mg/(kg day); offspring effects: F0=0.4 and F1> or =0.4 mg/(kg day). To distinguish between maternal and pup influences contributing to the perinatal mortality observed in the two-generation study, a follow-up cross-foster study was performed. Results of this study indicated that in utero exposure to PFOS causally contributed to post-natal pup mortality, and that pre-natal and post-natal exposure to PFOS was additive with respect to the toxic effects observed in pups.     

Developmental toxicity of perfluorooctane sulfonate (PFOS) is not dependent on expression of peroxisome proliferator activated receptor-alpha (PPAR alpha) 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 (PPAR alpha). The reduced postnatal survival of neonatal mice exposed to PFOA was recently shown to depend on expression of PPAR alpha. This study used PPAR alpha knockout (KO) and 129S1/SvlmJ wild type (WT) mice to determine if PPAR alpha 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 10.5mg PFOS/kg/day. KO females were dosed with 0.5% Tween-20, 8.5 or 10.5mg 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 10.5mg/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 PPAR alpha.     

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.     

Safety assessment of dietary diacylglycerol oil: A two-generation reproductive toxicity study in rats

Diacylglycerol (DAG) oil is a novel edible oil with similar taste and usability characteristics as conventional edible oils. Recent studies suggest that DAG oil may be helpful in the prevention and management of obesity. The objective of the present two-generation study was to evaluate potential adverse effects of DAG oil on reproductive processes. DAG oil was administered via gavage to rats (30/sex/group) for at least 70 days prior to mating, at dose levels of 0, 1.25, 2.5 or 5.0ml/kg/day (0, 1160, 2320 and 4630mg/kg/day). An additional group received a triacylglycerol (TAG) oil with a similar fatty acid composition to DAG oil. The rats were treated throughout the mating, gestation and lactation periods. Administration of DAG or TAG oil did not reveal any toxicologically significant effects on reproductive performance (mating, fertility and copulation/conception indices). DAG oil did not affect mean gestation lengths, the process of parturition, spermatogenic parameters, organ weights, histopathologic findings, mean numbers of pups born, implantation sites and unaccounted sites. F1 and F2 pup viability, live litter sizes, body weights, mean age of attainment of balanopreputial separation and vaginal patency were similar to those in the control group. Based on the results of this study, a dose level of 5.0ml/kg (4630mg/kg/day) was considered as the no-observed-adverse-effect level for reproductive and systemic toxicity, and neonatal toxicity.     

Behavioural effects of phenobarbitone II. Effects in nursing female mice

Phenobarbitone supplied at concentrations of 187.5 mg/l and 500 mg/l (50--60 mg/kg and 120--190 mg/kg daily) in the drinking fluid of mice throughout pregnancy and lactation did not affect gestation period, numbers born or resorbed or pup weights at birth and weaning. The higher dose caused significant retardation in eye-opening, development of forelimb extension, negative geotaxis, in appearance of washing and self-grooming behaviours and in cessation of suckling. The lower dose had no detectable effects. Ethological methods were used to examine spontaneous behaviour of nursing dams within home cages on days 1, 7, 14 and 21 postpartum. Treated dams showed differences in behaviour from controls, the most marked of which were increased levels of Maternal Behaviour and decreases in Non-Social Activity in the high-dose group at day 1, and continuance of pup Nursing in both treated groups and Nest Building in the high-dose group at day 21 when controls were ceasing these behaviours. At 21 days all treated dams also showed less Immobility than controls and high-dose dams a smaller amount of pup Social Investigation. Many behavioural differences at 21 days were related to developmental delay of treated pups. Overall, phenobarbitone did not impair maternal care.     

Tetrahydrofuran: two-generation reproduction toxicity in Wistar rats by continuous administration in the drinking water.

In a two-generation reproduction toxicity study, 25 male and 25 female Wistar rats per dose group and generation were exposed continuously to tetrahydrofuran in the drinking water for at least 70 days prior to and during mating, gestation, parturition and lactation to weaning, at concentrations of 0, 1000, 3000 or 9000 ppm (approximately 100, 300 and 700 mg/kg/day in males and females premating, 100, 300 and 800 mg/kg/day in females during gestation, and 200, 500 and 1300 mg/kg/day in females during lactation) through two successive generations. In both generations and sexes, water consumption was dose-relatedly reduced at all doses; food consumption and body weight were reduced at 9000 ppm. Necropsy kidney weights were increased in 9000 ppm F0 males. Pup body weight gain during lactation was reduced in both generations (F1 and F2 pups) and eye opening delayed in the first generation (F1 pups) at 9000 ppm; there were no treatment-related malformations. The NOAEL of tetrahydrofuran in drinking water is 9000 ppm for parental fertility and reproductive performance, and 3000 ppm for systemic parental and developmental toxicity.     

Refining the effects observed in a developmental neurobehavioral study of ammonium perchlorate administered orally in drinking water to rats. I. Thyroid and reproductive effects

A recent study further investigated the potential effects of maternal thyroid function and morphology on fetal development upon maternal exposure to ammonium perchlorate during gestation and lactation. Female Sprague-Dawley rats (25/group) were given continual access to 0 (carrier), 0.01, 0.1, 1.0, and 30.0 mg/kg-day perchlorate in drinking water beginning 2 weeks prior to cohabitation through lactation day 10. Maternal, fetal, and pup serum thyroid hormone (thyroid-stimulating hormone [TSH], triiodo thyronine [T(3)], thyroxine [T(4)]) levels and thyroid histopathology were evaluated on gestation day 21, and lactation days 5, 10, and 22. No effects of exposure were observed on cesarean-sectioning, litter parameters, or fetal alterations. Reproductive parameters, including gestation length, number of implants, litter size, pup viability, and lactation indices, were comparable among all groups. Thyroid weights of dams sacrificed on gestation day 21, and lactation days 10 and 22 were significantly increased at 30.0 mg/kg-day. Increased thyroid weights were observed in male and female pups as early as postpartum days 5 and 10, respectively. Changes in maternal and neonatal thyroid histopathology were detectable at 1.0 mg/kg-day exposure. The maternal no-observable-effect level (NOEL) was 0.1 mg/kg-day (follicular cell hyperplasia was present at 1.0 and 30.0 mg/kg-day). The developmental NOEL was less than 0.01 mg/kg-day; thyroid weights of postpartum day 10 pups were increased at all exposures. Colloid depletion at 1.0 and 30.0 mg/kg-day exposures and changes of hormone levels at all exposures were considered an adaptive effect and appeared reversible in the rodent.     

Exposure to perfluorooctane sulfonate during pregnancy in rat and mouse. II: postnatal evaluation.

The postnatal effects of in utero exposure to perfluorooctane sulfonate (PFOS, C8F17SO3-) were evaluated in the rat and mouse. Pregnant Sprague-Dawley rats were given 1, 2, 3, 5, or 10 mg/kg PFOS daily by gavage from gestation day (GD) 2 to GD 21; pregnant CD-1 mice were treated with 1, 5, 10, 15, and 20 mg/kg PFOS from GD 1 to GD 18. Controls received 0.5% Tween-20 vehicle (1 ml/kg for rats and 10 ml/kg for mice). At parturition, newborns were observed for clinical signs and survival. All animals were born alive and initially appeared to be active. In the highest dosage groups (10 mg/kg for rat and 20 mg/kg for mouse), the neonates became pale, inactive, and moribund within 30-60 min, and all died soon afterward. In the 5 mg/kg (rat) and 15 mg/kg (mouse) dosage groups, the neonates also became moribund but survived for a longer period of time (8-12 h). Over 95% of these animals died within 24 h. Approximately 50% of offspring died at 3 mg/kg for rat and 10 mg/kg for mouse. Cross-fostering the PFOS-exposed rat neonates (5 mg/kg) to control nursing dams failed to improve survival. Serum concentrations of PFOS in newborn rats mirrored the maternal administered dosage and were similar to those in the maternal circulation at GD 21; PFOS levels in the surviving neonates declined in the ensuing days. Small but significant and persistent growth lags were detected in surviving rat and mouse pups exposed to PFOS prenatally, and slight delays in eye opening were noted. Significant increases in liver weight were observed in the PFOS-exposed mouse pups. Serum thyroxine levels were suppressed in the PFOS-treated rat pups, although triiodothyronine and thyroid-stimulating hormone [TSH] levels were not altered. Choline acetyltransferase activity (an enzyme that is sensitive to thyroid status) in the prefrontal cortex of rat pups exposed to PFOS prenatally was slightly reduced, but activity in the hippocampus was not affected. Development of learning, determined by T-maze delayed alternation in weanling rats, was not affected by PFOS exposure. These results indicate that in utero exposure to PFOS severely compromised postnatal survival of neonatal rats and mice, and caused delays in growth and development that were accompanied by hypothyroxinemia in the surviving rat pups.     

Reproduction studies with 1α,25-dihydroxyvitamin D3 (calcitriol) in rats and rabbits

Reproduction and teratology studies were performed in rats and rabbits with 1α,25-dihydroxyvitamin D₃ (calcitriol). Dosages of 0.02, 0.08, and 0.3 μg/kg/day were administered orally as a solution in Neobee oil. In rat teratology studies, no substantial differences were noted between control animals and animals treated with calcitriol from Days 7 through 15 of gestation with respect to litter sizes, resorption rates, pup weights, or external, visceral, and skeletal abnormalities. No adverse effects on either fertility or neonatal development were noted in rat reproduction studies in which male and female rats were pretreated prior to mating through sacrifice on Day 13 of gestation or through lactation Day 21. No adverse effect on perinatal development was noted in litters from females treated from Day 15 of gestation through Day 21 of lactation. However, hypercalcemia and hypophosphatemia were observed in treated pregnant female rats at dosages of 0.08 and 0.3 μg/kg/day and increased serum urea nitrogen was observed at 0.3 μg/kg/day. Hypercalcemia calcemia was noted in pups from dams receiving 0.08 and 0.3 μg/kg/day calcitriol. There was no decrease in the percentage bone ash as determined on lactation Day 21 in either treated females or their pups as compared to controls. In rabbits treated from Days 7 through 18 of gestation with 0.3 μg/kg/day, $\text{3}\text{16}$ rabbits died. Other signs of toxicity included maternal weight loss, an increased resorption rate and neonatal mortality. Two litters at 0.3 μg/kg/day and 1 litter at 0.08 μg/kg/day contained fetuses with multiple abnormalities. These studies demonstrated that in pregnant animals the observed effects of calcitriol are characteristic of those reported for vitamin D₃. In rabbits, dosages of 0.3 μg/kg/day calcitriol produced maternal and fetotoxic effects.     

Lack of selective developmental neurotoxicity in rat pups from dams treated by gavage with chlorpyrifos.

Pregnant Sprague-Dawley rats were given chlorpyrifos (O:, O-diethyl-O:-[3,5,6-trichloro-2-pyridinyl] phosphorothioate; CPF) in corn oil by gavage from gestation day 6 (GD 6) through lactation day 10 (LD 10) at dosages of 0, 0.3, 1, or 5 mg/kg/day in a developmental neurotoxicity study that conformed to U.S. Environmental Protection Agency 1991 guidelines. GD 0 was the day when evidence of mating was observed and postnatal day 0 (PND 0) was the day of birth. Toxicity was limited to the highest dosage level (5 mg/kg/day) and, in the dams, consisted of muscle fasciculation, hyperpnea, and hyperreactivity. A nonsignificant overall trend toward weight gain and feed consumption was also observed in the high-dosage dams, with a statistically significant Group x Time interaction for reduced weight gain in the 5-mg/kg/day group near the end of gestation. Although many developmental indices were normal, pups from high-dosage dams had increased mortality soon after birth, gained weight more slowly than controls, and had several indications of slightly delayed maturation. The early deaths and delayed maturation were attributed to maternal toxicity, though a possible contributing role of direct pup toxicity in delayed development cannot be eliminated. In spite of the apparent delay in physical development, high-dosage pups tested just after weaning had normal learning and memory as tested on a T-maze spatial delayed-alternation task. Habituation, a primitive form of learning, was tested in 2 tasks (motor activity and auditory startle) and was not affected. No overt effects were noted in either dams or pups at 1 or 0.3 mg/kg/day. Based on these data, chlorpyrifos produced maternal and developmental toxicity in the 5-mg/kg/day-dosage group. There was no evidence of selective developmental neurotoxicity following exposure to chlorpyrifos.     

Combined repeated dose and reproductive/developmental toxicity screening test of the nitrophenolic herbicide dinoseb, 2-sec-butyl-4,6-dinitrophenol, in rats

In a combined repeated dose toxicity study with reproduction/developmental toxicity screening test, Crj:CD(SD)IGS rats were dosed with dinoseb, 2-sec-butyl-4,6-dinitrophenol, by gavage at 0 (vehicle), 0.78, 2.33, or 7.0 mg/kg bw/day. Six males per group were dosed for a total of 42 days beginning 14 days before mating. Twelve females per group were dosed for a total of 44-48 days beginning 14 days before mating to day 6 of lactation throughout the mating and gestation period. Recovery groups of six males per group and nonpregnant six females per group were dosed for 42 days followed by a 14-day recovery period. No deaths were observed in males of any dose group or in females of the recovery groups. At 7.0 mg/kg bw/day, eight females died and two animals were moribund during late pregnancy, and a significant decrease in body weight gain was found in both sexes. Hematocrit was significantly higher at 0.78 mg/kg bw/day and above in the main group males at the end of administration period. Reduction in extramedullary hematopoiesis in the spleen was significant at 2.33 mg/kg bw/day in the main group females. Sperm analysis revealed a decrease in sperm motility and an increase in the rates of abnormal sperm, abnormal tail, and abnormal head at 7.0 mg/kg bw/day. A number of dams delivered their pups and of dams with live pups at delivery was significantly lowered in the 7.0 mg/kg bw/day group. Based on these findings, the LOAEL for males and NOAEL for females were 0.78 mg/kg bw/day, and the NOAEL for reproductive/developmental toxicity was considered to be 2.33 mg/kg bw/day.     

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).     

Gestational and lactational exposure to heptachlor does not alter reproductive system development in rats

Like other organochlorine insecticides, heptachlor is lipophilic and accumulates in fatty tissues. Earlier studies suggested that in utero exposure to heptachlor decreased fertility in the offspring; neonatal exposure to the closely related insecticide chlordane reportedly delayed puberty and disrupted estrous cycling in females. We hypothesized that in utero and lactational exposure to heptachlor would disrupt the development of the reproductive system in males and females, resulting in altered timing of puberty and abnormal gonadal histology and reproductive hormone levels. Timed pregnant Sprague-Dawley rats were treated by oral gavage with heptachlor in corn oil at doses of 0.5 and 5.0 mg/kg or an equivalent volume of corn oil alone daily from gestational day 8 through post-natal day (PND) 21, the day of weaning (n = 7-8/group). Litters were standardized to 4 males and 4 females on the day of birth. Two of the dams in the 5.0 mg/kg/d group died. Pups in the highest dose group weighed significantly less than those in the other 2 groups on PND 0. All but 1 litter of the 5.0 mg/kg/d group died within the first 4 post-natal days. Age at eye opening was delayed with increasing heptachlor dose. There was no effect of treatment on pup weight gain in the surviving litters, on anogenital distance, age at puberty, nipple retention past the infantile period in males, estrous cycling, serum sex steroid concentrations, reproductive organ weights, or testicular or ovarian histology. These results suggest that heptachlor exposure during gestation and lactation does not disrupt development of the reproductive system in rats.     

Endocrine-disrupting activities in vivo of the fungicides tebuconazole and epoxiconazole.

The triazole fungicides tebuconazole and epoxiconazole were investigated for reproductive toxic effects after exposure during gestation and lactation. Rats were dosed with epoxiconazole (15 or 50 mg/kg bw/day) or tebuconazole (50 or 100 mg/kg bw/day) during pregnancy from gestational day (GD) 7 and continued during lactation until postnatal day (PND) 16. Some dams were randomly chosen for cesarean section at GD 21 to evaluate effects on sexual differentiation in the fetuses. Other dams delivered normally, and the pups were examined (e.g., anogenital distance [AGD] and hormone levels) at birth, at PND 13 or PND 16, and semen quality was assessed in adults. Both tebuconazole and epoxiconazole affected reproductive development in the offspring after exposure in utero. Both compounds virilized the female offspring as shown by an increased AGD PND 0. Furthermore, tebuconazole had a feminizing effect on male offspring as shown by increased nipple retention. This effect was likely caused by the reduced testosterone levels seen in male fetuses. Tebuconazole increased the testicular concentrations of progesterone and 17alpha-hydroxyprogesterone in male fetuses, indicating a direct impact on the steroid synthesis pathway in the Leydig cells. The high dose of epoxiconazole had marked fetotoxic effects, while the lower dose caused increased birth weights. The increased birth weights may be explained by a marked increase in testosterone levels in dams during gestation. Common features for azole fungicides are that they increase gestational length, virilize female pups, and affect steroid hormone levels in fetuses and/or dams. These effects strongly indicate that one major underlying mechanism for the endocrine-disrupting effects of azole fungicides is disturbance of key enzymes like CYP17 involved in the synthesis of steroid hormones.     

Two-generation reproduction study in rats given di-isononyl phthalate in the diet

The potential reproductive toxicity of di-isononyl phthalate (DINP: CAS RN 68515-48-0) was assessed in one- and two-generation reproductive toxicity studies. Groups of 30 male and female CRL : CD(SD)BR rats were given DINP via dietary administration at levels of either 0.0, 0.5, 1, or 1.5% (one-generation study) or 0.0, 0.2, 0. 4, or 0.8% (two-generation study). There were no changes in any of the classic reproductive parameters, i.e. mating, male or female fertility, fecundity, gestational index, or length of gestation in either study. The overall NOAELs for these effects were the highest Dietary Level (%)s tested, approximately 500 mg/kg/day in the two-generation study and 1000 mg/kg/day in the one-generation study. There were no testicular effects in parental animals exposed as juveniles and young adults at 960 mg/kg/day in the one-generation study. In the two-generation study, there were no testicular effects in either the P(1) males, exposed as juveniles and young adults or the P(2) (F(1)) offspring exposed in utero, through lactation, and continuously to terminal sacrifice. The NOAEL was 470 mg/kg/day. Offspring survival was reduced at the 1.5% level ( approximately 1100 mg/kg/day) but unaffected at the 1% level ( approximately 760 mg/kg/day). There were decreased offspring body weights both at postnatal day (PND) 0 and during lactation; however, the PND 0 effects were only clearly related to treatment at the 1.5% level. Weights of offspring during lactation were significantly reduced but within the historical control range at Dietary Level (%)s below 1%. As there was rapid recovery at the lower levels, even though treatment continued, the toxicologic significance is unclear. Adult survival was unaffected at any level in either study, but weight gain was significantly reduced at the 1% level ( approximately 600 mg/kg/day). Liver and kidney weights were elevated at Dietary Level (%)s above approximately 110 mg/kg/day, consistent with evidence from other studies of peroxisomal proliferation at these levels. This study showed that DINP treatment does not affect fertility or male reproductive development at doses of up to approximately 1000 mg/kg/day.     

An oral two-generation reproductive toxicity study of S-111-S-WB in rats

S-111-S-WB (CAS No. 72968-38-8), a mixture of perfluoro fatty acid ammonium salts, was administered daily via oral gavage to 30 Crl:CD(SD) rats/sex/group at 0.025, 0.125 and 0.6mg/(kgday) over two generations to assess potential reproductive toxicity. Reproductive performance, mean litter size, pup survival and pup weights were unaffected. Lower mean body weights were observed in 0.6mg/(kgday) group F(0) and F(1) males. Higher liver weights, correlating to hepatocellular hypertrophy in the 0.6mg/kg group, were noted for parental males in the 0.125 and 0.6mg/(kgday) groups, parental females in the 0.6mg/(kgday) group and F(1) pups in the 0.125 and 0.6mg/(kgday) groups. Higher kidney weights, correlating to renal tubule hypertrophy in the 0.6mg/kg group, were observed for parental males and females in the 0.125 and 0.6mg/(kgday) groups. Systemic exposure (measured only in females) to total S-111-S-WB was proportional to dose following 9 weeks of daily administration on the gestation day 19. Total S-111-S-WB concentration in the serum of male and female pups was 1.2-1.4-fold higher than in the dams 2h following administration to the dams on lactation day 13. A dosage level of 0.6mg/(kgday) was considered to be the no-observed-adverse-effect level (NOAEL) for reproductive function. A dosage level of less than 0.025mg/(kgday) was considered to be the NOAEL for F(0) and F(1) parental systemic toxicity based on microscopic hepatic findings in the males of all test article groups, and a dosage level of 0.025mg/(kgday) was considered to be the NOAEL for neonatal toxicity based on higher liver weights in the F(1) and F(2) pups at 0.125mg/(kgday) and higher.     

In Utero and Lactational Exposure to Fluoxetine in Wistar Rats: Pregnancy Outcomes and Sexual Development

This study evaluated the reproductive effects of fluoxetine exposure in utero and during lactation on pregnancy outcomes and the sexual development of offspring. Pregnant Wistar rats were treated daily with fluoxetine (0.4, 1.7 and 17 mg/kg/day) or distilled water by gavage from gestation day (GD) 7 to lactation day (LD) 21. A significant reduction in maternal body weight was observed during pregnancy and lactation in dams exposed to 17 mg/kg fluoxetine. Hormone analysis revealed an increase in progestagen and glucocorticoid metabolites on GD 15 and oestrogen and progestagen metabolites on LD 7 in dams treated with 17 mg/kg fluoxetine. Oestrogen metabolites also were increased on LD 7 in dams treated with 0.4 mg/kg fluoxetine. Besides that, an increase in the weight of the adrenal glands and a reduction in uterine weight in dams exposed to highest dose of fluoxetine were observed. Finally, pup birthweight and the viability and weaning indices also were reduced in animals exposed to 17 mg/kg fluoxetine. Overall, maternal hormonal changes were only observed at the highest dose tested, which also induced maternal and foetal toxicity. No significant changes were seen in dams or offspring exposed to therapeutic‐like doses.     

Reproductive toxicity studies with cis-(-)-2,3,4,4a,5,9b-hexahydro-2,8-dimethyl-1H-pyrido-[4,3-b]indole dipalmitate in rats

cis-(-)-2,3,4,4a,5,9b-Hexahydro-2,8-dimethyl-1H-pyrido-[4,3-b]indole dipalmitate (stobadin dipalmitate; in the following briefly called STB) a new prospective cardioprotective drug, was evaluated for effects on fertility, general reproductive performance, prenatal and peri-postnatal development in the rat. Doses of 5, 15 and 50 mg/kg/d were administered orally in aqueous suspension to rats in all studies. Daily treatment of male rats for 70 days before mating and female rats for 14 days before mating and during gestation and lactation had no adverse effects on fertility, survival rate and weight gains of parental animals or on prenatal and postnatal development of pups. There was only evidence of slight adult toxicity late in the experiment, significant increase of anomalous foetuses in both the 15 and 50 mg/kg/d doses and decreased body weight of the young at 50 mg/kg/d on day 21 post partum. Daily oral treatment of pregnant rats with STB throughout organogenesis (day 4 to 16) had no overt effects on dams or on embryo-foetal development, except of increased incidence of some skeletal variations in all treated groups. In the peri-postnatal toxicity study treatment of pregnant dams with STB continuously from day 15 of gestation through parturition and lactation had no adverse effects on reproductive parameters of dams or on survival and development of F1 offspring at any dose used. There were only signs of slight maternal toxicity at 50 mg/kg/d, which consisted of sedated behaviour, reduced liver weight and reversible histopathological changes in kidney tissue. The results of these studies did not reveal serious developmental hazard potentials of STB administered to rats in doses up to 50 mg/kg/d.     

Reproductive and repeated dose toxicity of cyclododecatriene (CDDT) in rats following oral (gavage) treatment

Cyclododecatriene (CDDT, CAS No. 4904-61-4) was administered daily by oral gavage to groups of Crl:CD (SD)IGS BR rats at dose levels of 0 (control), 30, 100, or 300 mg/kg/day. Female rats were dosed for four weeks premating, through mating, gestation, and lactation (a total of 55 to 63 days of treatment). Male rats were treated for 55 days (four weeks premating and through mating). Premating, body weights, food consumption, and clinical signs were recorded. Hematology, clinical chemistry, and urine analyses were conducted at the end of the premating period. A neurobehavioral test battery was conducted prior to and after four weeks of treatment. After the premating period, females were paired with males from the same groups for 1-2 weeks. Litters were delivered, pups were evaluated for structural integrity, and pup body weights were recorded on days 0 and 4 postpartum. Lactating females and their offspring were sacrificed on postpartum day 4. Selected organs were weighed and the tissues were examined microscopically from the lactating females. Offspring were examined for clinical abnormalities. A test substance-related reduction in body weight gain occurred in male rats administered 300 mg/kg/day. Decreased body weight gain in the 300 mg/kg/day males was accompanied by increased food consumption and decreased food efficiency. Females administered 100 or 300 mg/kg/day had test substance-related, significantly decreased body weight and body weight gain during gestation, that was accompanied by a significant increase in food consumption (300 mg/kg/day group only), and significantly decreased food efficiency. There were no test-substance related effects on clinical observations in males or females during the premating phase, or in females during gestation or lactation. Neurobehavioral parameters and motor activity were unaffected by CDDT-treatment. During this study, statistically significant treatment-related changes were observed in several clinical pathology parameters. The decreases in red cell mass (RBC, HGB, HCT) were minimal and, due to the magnitude, were not expected to result in biological effects. Similarly, minimally increased potassium and mildly decreased triglycerides were not of a magnitude to be biologically significant. Finally, changes in serum enzymes (AST, ALT, ALP), urea nitrogen, and serum protein occurred in directions that are not associated with toxicity. The changes in urine volume, urine concentration, and urea nitrogen may be the result of elevated glomerular filtration rate and altered tubular fluid flow, in the absence of any histopathological change. No effects on reproduction in parental males or females were produced by CDDT. Body weights of pups in the 300 mg/kg group were significantly decreased on postpartum days 0 and 4. There were no test-substance related effects on clinical observations, number of pups born, and the number of pups born alive, or the number of pups surviving through lactation day 4. The no-observed-adverse-effect level (NOAEL) for CDDT was 30 mg/kg/day based on decreased body weight and body weight gain, increased food consumption, and decreased food efficiency in females administered 100 or 300 mg/kg/day. The NOEL in pups was 100 mg/kg/day, based on decreased body weights of pups in the 300 mg/kg/day group during lactation.