Effects of amaranth on F1 generation mice.

The color additive, amaranth, was given in the diet to provide dietary levels of 0 (control), 0.03, 0.09 and 0.27%, from 5 weeks of age in F₀ generation mice to 9 weeks of age in F₁ generation mice, and some reproductive, developmental and behavioral parameters were measured. There was no effect on the parameters of litters, litter size, pup weight and litter weight. The body weight of pups during the lactation period in the treatment groups increased less significantly, and the survival index at postnatal day (PND) 21 of the amaranth 0.27% group was reduced. Developmental parameters, direction of swimming on PND 4 in male pups and olfactory orientation in each sex were significantly reduced in the treatment groups. The dose levels of amaranth in this study influenced some reproductive, developmental and behavioral parameters in mice.     

Reproductive and neurobehavioural effects in three-generation toxicity study of piperonyl butoxide administered to mice

Piperonyl butoxide (PB) was administered continuously to mice from 5 weeks of age in the F₀ generation to weaning of the F₂ generation. PB was administered in the diet at levels of 0 (control), 0.1, 0.2, 0.4 and 0.8%. Selected reproductive, developmental and behavioural parameters were measured. Litter size and litter weight were reduced in higher-dosed groups, and the body weight of the pups in the lactation period was reduced in dosed pups in each generation. The survival index at postnatal day 21 of the group receiving 0.8% PB was reduced in each generation. The developmental and behavioural parameters in the lactation period were little different from those of the controls, apart from olfactory orientation in the F₁ generation. However, in the F₂ generation mice, surface righting, cliff avoidance and olfactory orientation were adversely affected in treatment groups. The results suggest that PB had adverse effects on reproductive, developmental and behavioural parameters of mice, with increasing effects in subsequent generations of offspring.     

Reproductive and neurobehavioural effects of phloxine administered to mice

The colour additive phloxine was given in the diet to provide dietary levels of 0 (control), 0.1, 0.3 and 0.9%, from 5 wk of age of the F₀ generation to 8 wk of age of the F₁ generation in mice, and selected reproductive and neurobehavioural parameters were measured. There was little effect of phloxine on either litter size or weight, or sex ratio, whereas the body weight of the pups in the lactation period was significantly increased in all treatment groups. Among the neurobehavioural parameters measured, surface righting at postnatal day 4 of male pups was significantly reduced in all treatment groups. Some parameters of the motor activity of pups at 3 wk of age differed from those of the controls; in particular, the average speed of movement male pups was significantly reduced in all treatment groups. The dose levels of phloxine in this study produced a few adverse effects in reproductive and neurobehavioural parameters in mice.     

Reproductive and neurobehavioural effects of bis(2-ethylhexyl) phthalate (DEHP) in a cross-mating toxicity study of mice.

Bis(2-ethylhexyl) phthalate (DEHP) was given in the diet to provide levels of 0% (C) or 0.03% (T) from 5 weeks of age of the F0 generation to 9 weeks of age of the F1 generation in mice. At 9 weeks of age, each female was paired with one male from the same or another treatment groups (cross-mating: C/C, T/C, C/T, T/T), for a period of 5 days. The selected reproductive and neurobehavioural parameters were measured. There were no adverse effects of DEHP on either litter size, litter weight and sex ratio at birth. The average body weight of female offspring was significantly affected in group IV (T/T) at PND 14. In behavioural developmental parameters, swimming direction at PND 4 was significantly accelerated in group III (C/T) in female offspring. In movement activity of exploratory behaviour at 3 weeks of age, number of movement of male offspring was significantly affected in group IV (T/T). The dose level of DEHP in the present cross-mating study produced few adverse effects in reproductive and neurobehavioural parameters in mice.     

Reproductive and neurobehavioural toxicity study of erythrosine administered to mice in the diet.

Erythrosine was given in the diet to provide levels of 0 (control), 0.005, 0.015 and 0.045% from 5 weeks of age of the F(0) generation to 9 weeks of age of the F(1) generation in mice, and selected reproductive and neurobehavioural parameters were measured. There were no adverse effects of erythrosine on either litter size, litter weight or sex ratio at birth. The average body weight of the offspring was significantly increased in the middle-dose group in both sexes during the lactation period. In behavioural developmental parameters, any variables showed no significant adverse effects in either sex in the lactation period. In movement activity of exploratory behaviour, several parameters were significantly changed in the high-dose group, and those effects were dose related in adult females in the F(0) and F(1) generations and in male offspring in the F(1) generation. The dose level of erythrosine in the present study produced few adverse effects in reproductive and neurobehavioural parameters in mice.     

Reproductive and neurobehavioural toxicity study of bis(2-ethylhexyl) phthalate (DEHP) administered to mice in the diet.

Bis(2-ethylhexyl) phthalate (DEHP) was given in the diet to provide levels of 0 (control), 0.01, 0.03, and 0.09% from 5 weeks of age of the F0 generation to 9 weeks of age of the F1 generation in mice, and selected reproductive and neurobehavioural parameters were measured. There were no adverse effects of DEHP on either litter size, litter weight or sex ratio at birth. The average body weight of male offspring was significantly decreased in the low-dose group at birth. In behavioural developmental parameters, surface righting at PND 4 was significantly delayed in the low- and middle-dose group in female offspring, and those effects were slightly dose related (P < 0.05). Surface righting at PND 7 was significantly depressed in the high-dose group of male offspring, and those effects were significantly dose related (P < 0.001). That of female offspring was significantly depressed in the low-dose group. The dose level of DEHP in the present study produced few adverse effects in reproductive and neurobehavioural parameters in mice.     

Evaluation of the reproductive and developmental toxicity of aluminium ammonium sulfate in a two-generation study in rats

Aluminium ammonium sulfate (AAS) was tested for reproductive/developmental toxicity in a two-generation study. Male and female rats were continuously given AAS in drinking water at 0, 50, 500 or 5000 ppm. Water consumption was decreased in all AAS-treated groups, and the body weight of parental animals transiently decreased in the 5000 ppm group. In either generation, no compound-related changes were found in estrous cyclicity, sperm parameters, copulation, fertility and gestation index, number of implantations and live birth pups, sex ratios of pups or viability during the preweaning period. Male and female F1 pups in the 5000 ppm group showed a lower body weight on postnatal day 21, while there were no differences in the birth weight of F1 and F2 pups between the control and AAS-treated groups. Preweaning body weight gain in F2 males and females indicated a similar decreasing tendency at 5000 ppm. In F1 and F2 weanlings, the weight of the liver, spleen and thymus decreased at 5000 ppm, but no histopathological changes were found in these organs. In F1 females in the 5000 ppm group, vaginal opening was delayed slightly. There were no compound-related changes in male preputial separation or in other developmental landmarks. In behavioral tests conducted for F1 animals at 4-6 weeks of age, no compound-related changes were found in spontaneous locomotor activity and performance in a water-filled multiple T-maze. In conclusion, the NOAEL of AAS for two-generation reproductive/developmental toxicity was considered to be 500 ppm in rats. Considering the aluminium content in the basal diet, the total ingested dose of aluminium from drinking water and food in this 500 ppm group was calculated to be 5.35 mg Al/kg bw/day.     

Effects of tartrazine on exploratory behavior in a three-generation toxicity study in mice

Tartrazine was given to mice in the diet at levels of 0 (control), 0.05%, 0.15%, and 0.45% from 5 weeks of age of the F(0) generation to 9 weeks of age of the F(2) generation, and selected reproductive and neurobehavioral parameters were measured. In the F(1) generation, the development of swimming direction at postnatal day (PND) 7 was accelerated significantly in male offspring in a dose-related manner. Surface righting at PND 7 was affected significantly in female offspring in dose-related manner. Several variables in exploratory behavior showed significant tendencies to be affected in the treatment groups in male offspring at 3 weeks of age. In the F(2) generation, the development of swimming direction at PND 7 was accelerated significantly in the high-dosed group in male offspring. Time taken of olfactory orientation at PND 14 was accelerated significantly in male offspring in a dose-related manner. Several variables in exploratory behavior showed significant tendencies to be affected in the treatment groups in male offspring at 3 weeks of age, and in males at 8 weeks of age. The dose levels of tartrazine in the present study produced a few adverse effects on neurobehavioral parameters throughout generations in mice.     

Reproductive and neurobehavioural toxicity study of tartrazine administered to mice in the diet.

Tartrazine was given in the diet to provide levels of 0% (control), 0.05%, 0.15%, and 0.45% (approximately 83, 259, 773 mg/kg/day, respectively) from five weeks of age of the F0 generation to nine weeks of age of the F1 generation in mice, and selected reproductive and neurobehavioural parameters were measured. In movement activity of exploratory behaviour in the F0 generation, number of vertical activity was significantly increased in the middle-dose group in males. There were no adverse effects of tartrazine on either litter size, litter weight and sex ratio at birth. The average body weight of male offspring was significantly increased in the high-dose group and that of female offspring was significantly increased in the middle-dose group at birth. In behavioural developmental parameters, surface righting at PND 4 was significantly accelerated in the high-dose group in male offspring, and those effects were significantly dose-related in a trend test (P<0.01). Cliff avoidance at PND 7 was significantly accelerated in the middle-dose group in male offspring. Negative geotaxis at PND 4 was significantly delayed in the high-dose group in female offspring. Other variables measured showed no significant adverse effects in either sex in the lactation period. In movement activity of exploratory behaviour in the F1 generation, number of movement showed a significant tendency to be affected in the treatment groups in male offspring in a trend test (P<0.05). The dose level of tartrazine in the present study produced a few adverse effects in neurobehavioural parameters during the lactation period in mice. Nevertheless, the high-dose level were in excess of the ADI of tartrazine (0-7.5 mg/kgbw), and the actual dietary intake of tartrazine is presumed to be much lower. It would therefore appear that the levels of actual dietary intake of tartrazine is unlikely to produce any adverse effects in humans.     

Reproductive and neurobehavioural toxicity study of Ponceau 4R administered to mice in the diet.

Ponceau 4R was given to mice in the diet at levels of 0 (control), 0.12%, 0.24%, and 0.48% from 5 weeks of age of the F(0) generation to 9 weeks of age of the F(1) generation, and selected reproductive and neurobehavioural parameters were measured. There was no adverse effect of Ponceau 4R on litter size, litter weight or sex ratio at birth. The average body weight of male and female offspring was increased significantly in the high-dose group at postnatal days (PNDs) 0, 4 and 21. In behavioural developmental parameters, surface righting at PND 4 was affected significantly in the high-dose group in male offspring. Other variables measured showed no consistently significant adverse effect on either sex in the lactation period. In multiple water T-maze performance in the F(1) generation, the time taken was significantly longer than the control in the middle-dose and high-dose groups in males, and those effects were significantly dose-related (P<0.01). The dose level of Ponceau 4R in the present study produced no adverse effect on reproduction, and a few adverse effects on neurobehavioural parameters in mice. The non-observed adverse effect level (NOAEL) was presumed to be 0.12% in the diet (approximately 205mg/kg per day) for maze learning by males in the F(1) generation. Nevertheless, the middle-dose and high-dose levels were in excess of the acceptable daily intake (ADI) of Ponceau 4R (0-4.0mg/kg body weight), and the actual dietary intake of Ponceau 4R in humans is presumed to be much lower. It would appear, therefore, that the level of dietary intake of Ponceau 4R is unlikely to produce any adverse reproductive or neurobehavioural effect in humans.     

Two-generation reproductive toxicity study of aluminium sulfate in rats

In a two-generation reproductive toxicity study, male and female rats were given aluminium sulfate (AS) in drinking water at 0, 120, 600 or 3000 ppm. AS reduced water consumption in all treatment groups, and body weight was transiently decreased in the 3000 ppm group. In the F1 and F2 pups, preweaning body weight gain was inhibited at 3000 ppm, and the liver and spleen weight was decreased at weaning. At this dose, vaginal opening was slightly delayed. There were no compound-related changes in other reproductive/developmental parameters, including developmental neurobehavioral endpoints. The data indicated that the NOAEL of AS in this two-generation study is 600 ppm for parental systemic toxicity and reproductive/developmental toxicity. The total ingested dose of aluminium from drinking water and food (standard rat diet, containing 25-29 ppm of aluminium) combined for this 600 ppm group was calculated to be 8.06 mg Al/kg bw/day.     

EFFECTS ON PUBERTAL GROWTH AND REPRODUCTION IN RATS EXPOSED TO LEAD PERINATALLY OR CONTINUOUSLY THROUGHOUT DEVELOPMENT

The reproductive, endocrine, and growth effects of developmental lead exposure were assessed using a rat model in which 0.6% lead acetate (w/v) was administered in the drinking water ad libitum during different developmental periods to determine if lead actions were a result of direct effects of continuous exposure to the metal ion or secondary to disrupted neonatal "endocrine imprinting." Sprague Dawley rats were exposed to lead: (1) from gestational d 5 through birth; (2) during pregnancy and lactation; (3) during lactation only; (4) from birth through adulthood; or (5) from gestational d 5 through adulthood. Lead effects were measured on the development of aspects of the reproductive system, adult sex steroid levels, and growth rates in both male and female animals. The relative weights of male secondary sex organs in adult offspring were not significantly affected in any of the lead-treated groups. In contrast, female pups exposed to lead from birth through adulthood or from gestational day 5 through adulthood were observed to have significantly delayed vaginal opening and disrupted estrus cycling. These effects on female reproductive physiology were not observed in animals where lead exposure was confined only to pregnancy or lactation. Significant suppression of adult mean serum testosterone levels was only observed in male pups exposed to lead continuously from gestational age 5 d throughout life. Lead decreased birth weight in all animals exposed in utero and mean body weights were significantly decreased in all lead-treated groups up to weaning. Analysis of growth curves revealed that all lead-treated groups had significantly reduced growth rates during lactation. However, in addition, in male pups exposed to lead during pregnancy and lactation, from birth or from gestational age 5 d, growth rates were also significantly reduced during puberty. Postpubertal growth rates were unaffected in any lead-treated group. Thus, delayed female reproductive development and suppression of adult male serum testosterone concentration required continuous exposure to the heavy metal. Little evidence was observed for an alteration of "endocrine imprinting" by lead on either reproductive or growth parameters. Exposure during early development (pregnancy and lactation) resulted in no permanent effects in this model other than small (10%) decreases in the body weight of pups postpuberty.     

In utero exposure to arsenite contributes to metabolic and reproductive dysfunction in male offspring of CD-1 mice

In utero exposure to arsenite (iAs) is known to increase disease risks later in life. We investigated the effect of in utero exposure to iAs in the drinking water on metabolic and reproductive parameters in male mouse offspring at postnatal and adult stages. Pregnant CD-1 mice were exposed to iAs (as sodium arsenite) in the drinking water at 0 (control), 10 ppb (EPA standard for drinking water), and 42.5 ppm (tumor-inducing dose in mice) from embryonic day (E) 10–18. At birth, pups were fostered to unexposed females. Male offspring exposed to 10 ppb in utero exhibited increase in body weight at birth when compared to controls. Male offspring exposed to 42.5 ppm in utero showed a tendency for increased body weight and a smaller anogenital distance. The body weight in iAs-exposed pups continued to increase significantly compared to control at 3 weeks and 11 weeks of age. At 5 months of age, iAs-exposed males exhibited greater body fat content and glucose intolerance. Male offspring exposed to 10 ppb in utero had higher circulating levels of leptin compared to control. In addition, males exposed to 42.5 ppm in utero exhibited decreased total number of pups born compared to controls and lower average number of litters sired over a six-month period. These results indicate that in utero exposure to iAs at either human relevant concentration or tumor-inducing concentration is a potential cause of developmental origin of metabolic and reproductive dysfunction in adult male mice.     

The reproductive toxicology of ammonium perfluorooctanoate (APFO) in the rat

Ammonium perfluorooctanoate (APFO) is a surfactant used primarily as an aid in processing various fluoropolymers. Many toxicology and epidemiological studies have been conducted with APFO; however, no specific information regarding functional reproduction was previously available. Therefore, the potential reproductive toxicity of APFO across two generations of offspring was studied using current EPA OPPTS 870.3800 guidelines. Male and female Sprague-Dawley rats were dosed orally with 0, 1, 3, 10, or 30 mg/kg APFO. Parental (P) generation rats ( approximately 6 weeks old) were dosed at least 70 days prior to mating and until sacrificed (after mating for male rats; after weaning for female rats). F(1)-generation rats were dosed similarly, beginning at weaning. The F(2)-generation pups were maintained through 22 days of lactation. Reproductive parameters evaluated in P- and F(1)-generation rats included estrous cycling, sperm number and quality, mating, fertility, natural delivery, and litter viability and growth. Age at sexual maturation in F(1), anogenital distance in F(2), and presence of nipples (males) in F(2)-generation pups were also determined. Feed consumption, body-weight gain, selected organ-weights, gross pathology and appropriate histopathology were evaluated. Reproductive endpoints including mating, fertility, and natural delivery were not affected in either generation. P- and F(1)-generation male rats showed decreased body weight, and liver and kidney weight increases at all doses. The 30 mg/kg F(1)-generation pups had decreased birth weight. Viability was reduced in the 30 mg/kg F(1)-generation pups in apparent relationship to reduced body weight at birth and weaning; however, F(2)-generation pups at 30 mg/kg, although somewhat lighter, did not show a loss in viability. Preputial separation and vaginal opening were somewhat delayed at 30 mg/kg, but these rats went on to show normal reproductive performance. No-observed-adverse-effect-levels were >30 mg/kg for reproductive function of P- and F(1)-generation rats, 10 mg/kg for F(1)-generation pup mortality, birth weight, and sexual maturation, and less than 1mg/kg for male body-weight and organ-weight changes.     

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.     

Multigenerational reproductive study of genistein (Cas No. 446-72-0) in Sprague-Dawley rats (feed study)

Genistein is a naturally occurring isoflavone that interacts with estrogen receptors and multiple other molecular targets. Human exposure to genistein is predominantly through consumption of soy products, including soy-based infant formula and dietary supplements. Consumption of soy and genistein has been associated with a variety of beneficial effects in animals and humans, but concerns have also been raised concerning potential adverse effects of genistein, particularly with regard to reproductive toxicity and the induction or potentiation of carcinogenesis, due primarily to its weak estrogenic activity. Because of these concerns, genistein was selected as one of the compounds to be examined in a protocol utilizing Sprague-Dawley rats to evaluate the effects of multigenerational and long-term exposures to doses of estrogenic agents that produce subtle reproductive tract lesions in developmentally exposed Sprague-Dawley rat pups. Results from the multigenerational reproductive toxicology feed study are reported in this report, and results of the 2-year feed study are reported separately (NTP, 2008a). Data from a preliminary reproductive dose range-finding feed study (NTP, 2007) that utilized exposure concentrations of up to 1,250 ppm genistein were used to select dietary exposure concentrations of 0, 5, 100, and 500 ppm for the current study. These dietary doses resulted in ingested genistein doses of approximately 0, 0.3, 7, or 35 mg genistein/kg body weight per day for males and 0, 0.5, 10, or 51 mg/kg per day for females during the time that the rats were directly consuming dosed feed. The current study was a multigenerational study (F(0) through F(4), with F(5) litters terminated at weaning) focused on reproductive endpoints. Animals were continuously exposed to genistein from the time that the F(0) generation was 6 weeks old through weaning of the F(3) generation, and animals of the F(0) through F(4) generations were sacrificed and necropsied on postnatal day 140 (PND 140). Dosed feed was removed from the F(3) pups at the time of weaning, and this generation and subsequent generations were maintained on control feed for the remainder of the study. For this study, 140 animals of each sex were obtained from the NCTR CD (Sprague-Dawley) rat colony at weaning and placed on a soy- and alfalfa-free diet that was used throughout the study in an attempt to maintain consistently low background exposure to phytoestrogens. Thirty-five animals per sex were assigned to exposure groups by a weight-ranked randomization procedure prior to the start of dietary exposure of the parental (F(0)) generation at 6 weeks of age. At the time of mating, males were paired with females from the same exposure group, and they were housed together until evidence of successful mating was detected or for a maximum of 14 days. Litters were randomly standardized to four males and four females on PND 2, and 25 litters per exposure group and their associated sires and dams were randomly selected to continue on study to produce the next generation and then necropsied at termination at 20 weeks of age (PND 140). Similar procedures were used to produce each generation. Results of the current study are summarized below. In the postweaning period, exposure to 500 ppm genistein reduced body weights predominantly in females of generations in which rats were ingesting the compound throughout adulthood (F(0) through F(2)). In the unexposed F(4) generation, female body weight was also depressed, although to a lesser extent than in the earlier generations. In the F(1) generation, postweaning body weights were reduced in all 100 and 500 ppm groups, with a more pronounced effect in the females. While pup birth weights were not significantly affected by genistein in the F(1) through F(4) generations (with the exception of 100 ppm males in the F(1) generation), both sexes showed depressed body weight gains during the preweaning period in the 500 ppm groups in all of these generations. Male pup preweaning body weight gains were also depressed in the 5 and 100 ppm groups in the F(1) generation. In the unexposed F(5) generation, pup birth weights in all exposed groups of both sexes were significantly lower than those in the controls, although it seems likely that this is a chance observation rather than a carryover effect from exposures in earlier generations. Measures of fertility were not adversely affected by genistein except for litter size. Litter size of the 500 ppm group in the F(2) generation was significantly smaller than that in the corresponding control group. The litter sizes in the F(1), F(2), and F(3) generations showed negative exposure concentration trends. Male and female 500 ppm pups in the F(1) generation had slightly reduced anogenital distances (AGDs) relative to controls when covaried by body weight. Female pups also had reduced AGDs in the F(2) (500 ppm) and F(3) (100 ppm) generations, although the statistical significance was dependent on the analysis method applied. Females exposed to 500 ppm showed an accelerated time of vaginal opening (approximately 3 days) in the F(1) and F(2) generations, while the 5 ppm group showed an earlier time of vaginal opening (1.3 days) in the F(3) generation. Body weight at vaginal opening was lower in 500 ppm females of the F(1) through F(3) generations and in the 5 ppm females of the F(1) generation. When examined shortly after vaginal opening, estrous cycles of 500 ppm females in the F(1) and F(2) generations were significantly longer (approximately 3 days and 1 day, respectively) than those of their respective control groups. Other estrous cycle disturbances (with the exception of decreased time in diestrus for 100 ppm females in the F(4) generation) were confined to the 500 ppm group of the F(1) generation and included reduced time in proestrus and an increase in the number and percentage of aberrant cycles. When the estrous cycles of older animals were examined prior to termination, the sole significant effects were a decreased time in estrus and increased time in diestrus in 5 ppm females of the F(2) generation and an increased number of abnormal cycles in 500 ppm females of the F(3) generation. No effects of genistein on male sexual development were noted with the exception of an increased time to testicular descent in 500 ppm males of the F(3) generation. Significant organ weight effects in both sexes were largely confined to single exposed groups in single generations; no clear patterns indicating toxicity to reproductive or nonreproductive organs were observed. Exposure-related microscopic lesions were confined to males, with the mammary gland and kidney affected. Incidences of mammary gland alveolar/ductal hyperplasia were significantly increased in 500 ppm males in the F(0) through F(2) generations and in 100 ppm males in the F(1) and F(2) generations. In the F(3) generation, a significant positive linear exposure concentration trend in the incidences of mammary gland hyperplasia occurred, but no exposed group differed significantly from the controls in pairwise comparisons. The more pronounced effect of genistein on the incidences of male mammary gland hyperplasia in the continuously exposed F(1) and F(2) generations as compared to the late adolescent and adult exposures of the F(0) generation and the preweaning-only exposure of the F(3) generation indicates that both developmental and adult exposures contribute to the maintenance of this effect into adulthood. Statistically significant effects of genistein on the incidences of generally minimal to mild kidney lesions in males were confined to the continuously exposed F(1) and F(2) generations. Incidences of renal tubule mineralization were significantly increased in 100 and 500 ppm males in the F(1) and F(2) generations, and incidences of inflammation and renal tubule regeneration were significantly increased in 500 ppm males in the F(1) generation. In addition to the results reported above for animals from the main study, ancillary studies were conducted with pups derived from the current study or from animals treated under similar conditions. These results have been reported elsewhere (Appendix P) and are not presented in detail in this report. Of particular importance are the data on blood and tissue genistein concentrations obtained from adult animals in the F(1) generation (Chang et al., 2000), from dams and fetuses (Doerge et al., 2001), and from dams and nursing pups (Doerge et al., 2006). These data provide measures of the internal dose resulting from the dietary exposure concentrations used in the current study and indicate that while fetal and adult exposures to genistein were at concentrations relevant to the full range of human exposures, only very low exposures were achieved during the early neonatal period when the pups were receiving exposures exclusively from the milk. The minimal exposure to genistein during this critical developmental period must be considered in the interpretation of the data derived from the current study. In summary, although genistein did show adverse effects with dietary exposures of 100 or 500 ppm, there were no clear adverse effects on the reproductive or developmental parameters measured at genistein concentrations ranging from less than 1 ppm (control diet) to 100 ppm, a range of doses producing serum concentrations achievable from the phytoestrogen content of human diets. There were few clear, overtly toxic effects that carried over across directly exposed generations or appeared to be imprinted to carry over into unexposed descendents under the conditions of exposure in this study. (ABSTRACT TRUNCATED).     

Reproductive toxicity studies in rats with rimexolone, a corticoid ophthalmic suspension.

Rimexolone is a potent anti-inflammatory corticosteroid with a lower potential for elevating intraocular pressure, relative to other ophthalmic steroids, and is indicated for postsurgical inflammation and uveitis. Fertility and peri/postnatal toxicities were evaluated at oral gavage doses of 50, 150 or 500 mg/kg, and developmental toxicity at 100, 500, or 1000 mg/kg. In the fertility study, male rats were treated daily beginning 4 weeks prior to mating and females were treated daily beginning 2 weeks prior to mating, and through gestation day 6. Females were necropsied on gestation day 15 and males were necropsied after 10 weeks of exposure. In males, dose-related reductions in mean body weights, body weight gains, and food consumption occurred in all groups. In the 500 mg/kg females, mean body weights were reduced during gestation, and there was an increase in early resorptions and concomitant decrease in viable fetuses at this level. There were no effects on copulation or fertility indices, or on the number of corpora lutea and implantation sites. The no-observed-effect level (NOEL) for fertility and reproductive effects was 150 mg/kg. In the developmental toxicity study, female rats were treated daily from gestation days 6 through 17, necropsied on gestation day 20 and fetuses were evaluated. Maternal toxicity occurred at 500 and 1000 mg/kg as indicated by reduced maternal body weights and body weight gains. However, there was no indication of a developmental effect on fetuses due to rimexolone. The NOEL was 1000 mg/kg for the developing fetuses. In the peri/postnatal toxicity study, female rats were treated daily from gestation day 6 through lactation day 20 and necropsied. F1 developmental and behavioral parameters were evaluated. Selected F1 animals were mated at 12 weeks, allowed to deliver, and necropsied on lactation day 21. At 500 mg/kg, F0 maternal body weights were reduced during gestation and lactation, and F1 pup weights were reduced during lactation and the growth phase. There were no effects on the F1 fertility or reproductive capabilities, or on F2 developmental parameters. The NOEL for the F0 females and F1 offspring was 150 mg/kg. Together, these studies indicate that, unlike some corticosteroids, rimexolone does not produce developmental or reproductive toxicity in rats.     

Developmental and reproductive toxicity evaluation of toluene vapor in the rat. I. Reproductive toxicity

The reproductive toxicity of toluene was evaluated in a 2-generation test in which male and female Sprague–Dawley rats, parental (F0) and first generation (F1), were exposed to toluene via whole body inhalation, 6 h/day, 7 days/week for 80 days premating and 15 days of mating at concentrations of 0, 100, 500 and 2000 ppm (0, 375, 1875 and 7500 mg/m³). Toluene was administered at 2000 ppm to both sexes, or to females or males only to be mated with untreated partners. Pregnant females at all dose levels were exposed from gestation day (GD) 1–20 and lactation day (LD) 5–21. At LD5, females were removed from their litters for daily exposure and returned when 6 h of exposure was completed. F1 pups selected to produce the F2 generation were treated for 80 days beginning immediately after weaning (LD21) and initially mated at a minimum of 100 days of age. F2 pups were not exposed to toluene by inhalation.

Toluene exposure did not induce adverse effects on fertility, reproductive performance, or maternal/pup behaviors during the lactation period in males and females of the parental or first generation, but did inhibit growth in F1 and F2 offspring in the 2000 ppm (both sexes treated) and 2000 ppm (females only treated) groups. Caesarean section of selected 2000 ppm (both sexes treated) dams at GD20 showed reduced fetal body weight and skeletal variations. Exposure to toluene caused decreased pup weights throughout lactation in F1 and F2 2000 ppm (both sexes treated), and 2000 ppm (females only treated) groups. Exposure at 2000 ppm to male parents only did not induce similar weight inhibition in offspring. The toluene offspring NOAEL is 500 ppm in groups in which maternal animals were exposed, and 2000 ppm for male only treated groups.     

Reproductive and developmental toxicity in F1 Sprague-Dawley male rats exposed to di-n-butyl phthalate in utero and during lactation and determination of its NOAEL

Di-n-butyl phthalate (DBP) is one of the commonly used plasticizers in China. DBP can enter the environment and organisms through various routes and then affect reproductive and developmental processes of the organism and its descendants (mainly affecting male offspring). It is known that animals are sensitive to exposure of DBP in utero and during lactation. In the present study, pregnant rats were treated with different doses of DBP (0, 50, 250, and 500 mg/kg body weight/day) by daily gavage from GD1 to PND21. The developmental condition of F1 rats and the reproductive system of mature F1 male rats were monitored. DBP had no obvious effect on pregnant rats; however, it reduced several parameters including birth weight, number of live pups per litter, body weight gain and male anogenital distance. Severe damage to the reproductive system of mature F1 male rats included testicular atrophy, underdeveloped or absent epididymis, undescended testes, obvious decline of epididymal sperm parameters, total sperm heads per g testis, decrease of organ/body weight ratio of epididymis and prostate, and was observed in the group treated with 250 mg/kg BW/day and higher. These results showed that the male reproductive system was the main target organ of DBP exposure. The NOAEL (no observable adverse effect level) for developmental toxicity of DBP was established based on pup body weight and male reproductive lesions at 50 mg/kg BW/day. Accordingly, the RfD for human exposure to DBP through oral intake was recommended as 500 mg/kg BW/day.     

Effects of bis(2-ethylhexyl) phthalate (DEHP) on secondary sex ratio of mice in a cross-mating study.

Bis(2-ethylhexyl) phthalate (DEHP) was given in the diet to provide levels of 0 (C) or 0.03% (T) from 5 weeks of age of the F(0) generation to birth of the F(1) generation in mice. At 9 weeks of age, each female was paired with one male from the same or another treatment groups (cross-mating: C/C, T/C, C/T, T/T), for a period of 5 days. The males were removed from females after 5 days, and the females were allowed to carry their litters to term and deliver. There were no adverse effects of DEHP on either litter size, litter weight and sex ratio at birth. The average body weight of male offspring was significantly increased in all treatment groups at birth. There were no adverse effects of DEHP on female offspring weight at birth. The dose level of DEHP in the present study produced no adverse effects on secondary sex ratio, which meant sex ratio at birth, in mice.