Inhalation developmental toxicity and reproduction studies with cyclohexane

The reproductive and developmental toxicity of cyclohexane was assessed in a two-generation reproduction study with Crl:CD BR rats and in developmental toxicity studies with Crl:CD BR rats and Hra:(NZW)SPF rabbits. The animals were exposed whole-body to atmospheric concentrations of 0, 500, 2000, or 7000 ppm cyclohexane. In the two-generation reproduction study, parental effects included statistically significantly lower mean body weight, overall mean body weight gain, and overall mean food efficiency for P1 and F1 females of the 7000 ppm level and statistically significantly lower mean body weight for F1 males of that level. Adult rats exposed to 2000 ppm cyclohexane and above exhibited a transient diminished or absent response to a sound stimulus while in the chambers during exposure. Mean pup weight was statistically significantly lower than control from lactation day 7 throughout the remainder of the 25-day lactation period for both F1 and F2 7000 ppm litters. Changes observed at 500 ppm were either considered not to be compound related or not adverse. Therefore, the systemic-toxicity no-observed-effect level (NOEL) was 500 ppm and the reproductive NOEL was 2000 ppm. The reproductive NOEL was based solely on the decreased pup weights in both the F1 and F2 generations observed at 7000 ppm. In the developmental toxicity studies, only the rats showed evidence of maternal toxicity. For rats in the 7000 ppm group, statistically significant reductions were observed in overall maternal body weight gain and overall maternal food consumption for the treatment period. Rats exposed to 2000 ppm cyclohexane and above again exhibited a transient diminished or absent response to a sound stimulus while in the chambers during exposure. Therefore, for rats, the maternal no-observed-effect level (NOEL) was 500 ppm. In the rabbit developmental toxicity study, no compound-related maternal effects were observed at concentration levels of 7000 ppm and below. Therefore, the maternal NOEL for rabbits was 7000 ppm. No compound-related evidence of developmental toxicity was observed at any test concentration in either species. Therefore, the developmental NOEL for both species was 7000 ppm, the highest concentration tested.     

Reproductive toxicity evaluation of dietary butyl benzyl phthalate (BBP) in rats

Butyl benzyl phthalate (BBP) was administered in the diet at 0, 750, 3750, and 11,250 ppm ad libitum to 30 rats per sex per dose for two offspring generations, one litter/breeding pair/generation, through weaning of F2 litters. Adult F0 systemic toxicity and adult F1 systemic and reproductive toxicity were present at 11,250 ppm (750 mg/kg per day). At 11,250 ppm, there were reduced F1 and F2 male anogenital distance (AGD) and body weights/litter during lactation, delayed acquisition of puberty in F1 males and females, retention of nipples and areolae in F1 and F2 males, and male reproductive system malformations. At 3750 ppm (250 mg/kg per day), only reduced F1 and F2 offspring male AGD was present. There were no effects on parents or offspring at 750 ppm (50 mg/kg per day). The F1 parental systemic and reproductive toxicity no observable adverse effect level (NOAEL) was 3750 ppm. The offspring toxicity NOAEL was 3750 ppm. The offspring toxicity no observable effect level (NOEL) was 750 ppm, based on the presence of reduced AGD in F1 and F2 males at birth at 3750 ppm, but no effects on reproductive development, structures, or functions.     

Two-generation reproduction study by dosing with glutaraldehyde in the drinking water of CD rats

Adult male and female CD rats (F0) were dosed with glutaraldehyde (GA; CAS number 111-30-8) in drinking water at concentrations of 0 (controls), 50, 250, or 1000 ppm for a 10-wk prebreed period and through mating, gestation, and lactation. Resultant F1 offspring, selected to be parents of the next generation, were continued on the same regime from prebreed through lactation. Twenty-eight parental animals per sex per generation for each dose group were evaluated for clinical signs, body weight (absolute and gain), and water and food consumption. The offspring were evaluated for survival and body weight to weaning. Necropsy and light microscopic examination of removed tissues were conducted in all F0 and F1 parents and in 10 offspring/sex/group/generation. Average daily consumptions of GA (as mean +/- SD) for the low, intermediate, and high concentrations were respectively 4.25 +/- 0.87, 17.50 +/- 4.16, and 69.07 +/- 14.58 mg/kg/d for F0 parental males, and 6.68 +/- 0.78, 28.28 +/- 4.09, and 98.37 +/- 11.71 mg/kg/d for F0 parental females. The corresponding values for the F1 parents were 4.53 +/- 1.02, 21.95 +/- 4.88, and 71.08 +/- 16.21 mg/kg/d for males and 6.72 +/- 0.84, 29.57 +/- 5.41, and 99.56 +/- 16.72 mg/kg/d for females. There were no effects on parental fertility and mating performance or on pup viability and litter size in any generation. No apparent treatment-related histopathology was seen in parents or offspring. Parental body weights and body weight gains were significantly reduced at 1000 ppm at a few isolated time periods, particularly during prebreed. Food consumption was significantly reduced at 1000 ppm for F0 and F1 parents during the prebreed and gestation periods, and at 250 ppm for F0 males during prebreed and gestation and F1 females during gestation and lactation. Water consumption by the F0 and F1 parents of the 250 at 1000 ppm groups was reduced throughout the prebreed period. At 1000 ppm, average litter weights were reduced over lactation d 21-28 for the F1 and F2 offspring. The no-observed-effect level (NOEL) for adult toxicity was 50 ppm and for offspring 250 ppm. There were no indications of reproductive toxicity, and the NOEL for this study was therefore > 1000 ppm.     

INHALATION DEVELOPMENTAL TOXICITY AND REPRODUCTION STUDIES WITH CYCLOHEXANE

The reproductive and developmental toxicity of cyclohexane was assessed in a two-generation reproduction study with Crl:CD® BR rats and in developmental toxicity studies with Crl:CD®BR rats and Hra:(NZW)SPF rabbits. The animals were exposed whole-body to atmospheric concentrations of 0, 500, 2000, or 7000 ppm cyclohexane. In the two-generation reproduction study, parental effects included statistically significantly lower mean body weight, overall mean body weight gain, and overall mean food efficiency for P₁ and F₁ females of the 7000 ppm level and statistically significantly lower mean body weight for F¹ males of that level. Adult rats exposed to 2000 ppm cyclohexane and above exhibited a transient diminished or absent response to a sound stimulus while in the chambers during exposure. Mean pup weight was statistically significantly lower than control from lactation day 7 throughout the remainder of the 25-day lactation period for both F₁ and F₂ 7000 ppm litters. Changes observed at 500 ppm were either considered not to be compound related or not adverse. Therefore, the systemic-toxicity no-observed-effect level (NOEL) was 500 ppm and the reproductive NOEL was 2000 ppm. The reproductive NOEL was based solely on the decreased pup weights in both the F₁ and F₂ generations observed at 7000 ppm. In the developmental toxicity studies, only the rats showed evidence of maternal toxicity. For rats in the 7000 ppm group, statistically significant reductions were observed in overall maternal body weight gain and overall maternal food consumption for the treatment period. Rats exposed to 2000 ppm cyclohexane and above again exhibited a transient diminished or absent response to a sound stimulus while in the chambers during exposure. Therefore, for rats, the maternal no-observed-effect level (NOEL) was 500 ppm. In the rabbit developmental toxicity study, no compound-related maternal effects were observed at concentration levels of 7000 ppm and below. Therefore, the maternal NOEL for rabbits was 7000 ppm. No compound-related evidence of developmental toxicity was observed at any test concentration in either species. Therefore, the developmental NOEL for both species was 7000 ppm, the highest concentration tested.     

Two-generation reproductive toxicity study of inhaled acrylonitrile vapors in Crl:CD(SD) rats

To assess the effects of acrylonitrile (AN) exposure on reproduction, Sprague-Dawley rats (25/sex/group) were exposed to vapor atmospheres of AN via whole-body inhalation at concentrations of 0, 5, 15, 45 (two offspring generations) and 90 ppm (one offspring generation), 6 h daily, 1 litter/generation, through F2 weanlings on postnatal day 28. After approximately 3 weeks of direct exposure following weaning, exposure of the F1 animals at 90 ppm was terminated due to excessive systemic toxicity in the males. There were no exposure-related mortalities in adult animals, no functional effects on reproduction or effects on reproductive organs, and no evidence of cumulative toxicity or of enhanced toxicity in pregnant and lactating dams or in developing animals. Adult systemic toxicity was limited to body weight and/or food consumption deficits in both sexes and generations (greater in males) at 45 and 90 ppm and increased liver weights in the 90 ppm F0 males and females and 45 ppm F1 males. Neonatal toxicity was expressed by F1 offspring weight decrements at 90 ppm. Clinical signs of local irritation during and immediately following exposure were observed at 90 ppm. Microscopic lesions of the rostral nasal epithelium, representing local site-of-contact irritation, were observed in some animals at 5 to 45 ppm. The no-observed-adverse-effect level (NOAEL) for reproductive toxicity over two generations and neonatal toxicity of AN administered to rats via whole-body inhalation was 45 ppm. The NOAEL for reproduction was 90 ppm for the first generation. The NOAEL for parental systemic toxicity was 15 ppm.     

Three-generation reproduction study of rats receiving acrylonitrile in drinking water

Acrylonitrile, a high volume organic chemical, was tested for reproductive effects in a three generation drinking water study with two matings per generation. Sprague-Dawley rats were exposed to acrylonitrile in drinking water at 0, 100, or 500 ppm. This corresponds to 0, 11+/-5 and 37+/-10 mg/kg, respectively, for males and 0, 20+/-3 and 40+/-8 mg/kg per day for the females, respectively. Water consumption was reduced in F0 rats in the 100 and 500 ppm groups. At 500 ppm, acrylonitrile reduced body weight gain and food intake of the first generation parental rats (F0). These parameters were not investigated at subsequent generations. The pup survival (both viability and lactation indices) was reduced at the 500 ppm treatment level in both matings of all three generations. Fostering the 500 ppm pups onto untreated mothers following the second mating lessened mortality, suggesting a maternal effect consistent with decreased water consumption. There was no remarkable change in the reproductive capacity in any of matings in rats at the 100 ppm concentration. In contrast, in all three generations, the body weights of the pups of the 500 ppm treatment level were reduced on Day 21 at both matings. No adverse findings were observed in the tissues of a limited number of third generation weanlings (F3b) upon gross and microscopic evaluation. No effect on the sciatic nerve was evident among the adult female rats held for 20 weeks after weaning of the second litter. There was a dose-related effect of acrylonitrile on gross masses in female rats at each parental generation held 20 weeks after the weaning of the second litter. Histopathological evaluation of these dams showed an increase in astrocytomas and zymbal gland tumors.     

Two-generation reproduction and developmental neurotoxicity study with sodium chlorite in the rat

The potential for sodium chlorite to produce reproductive toxicity, developmental neurotoxicity and alterations in hematology and thyroid hormones was evaluated in Sprague-Dawley rats administered sodium chlorite in the drinking water continuously for two generations. The F(0) generation animals (30 of each gender per group) and F(1) generation animals (25 of each gender per group) selected to rear the F(2) generation were allowed free access to drinking water containing 0, 35, 70 or 300 ppm sodium chlorite for a 10-week prebreed period, through mating for males and through mating, gestation and lactation for females. These drinking water concentrations corresponded to sodium chlorite doses of approximately 4, 8 and 30 mg kg(-1) day(-1) for males and 5, 10 and 39 mg kg(-1) day(-1) for females, respectively. Evaluations included standard reproductive and postnatal indices, sperm morphology and motility, estrous cyclicity, a functional observational battery, motor activity, auditory startle, swim maze, hematology, serum thyroid hormone analyses and histopathology of reproductive and nervous system tissues. Sodium chlorite resulted in a decrease in water consumption in all groups and a decrease in food consumption and body weights in the 70 and 300 ppm groups. There was no evidence of reproductive toxicity. Pup body weight was decreased in the 300 ppm group and small delays were observed in the time to preputial separation and vaginal opening. Mild anemia and mild methemoglobinemia were observed for animals in the 300 ppm group. Thyroid hormone levels were not affected by treatment. Changes to the nervous system were limited to small decreases in amplitude of auditory startle response for postnatal day (PND) 25 pups in the 70 and 300 ppm groups and a small decrease in absolute brain weight for PND 11 pups in the 300 ppm group. These effects were considered to be of questionable neurotoxicological significance. Based on the results of this study, the no-observed-effect level (NOEL) for effects on reproduction and thyroid hormones is 300 ppm. The no-observed-adverse-effect levels (NOAEL) for hematological toxicity and neurotoxicity are considered to be 70 and 300 ppm, respectively.     

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.     

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).     

Oral (drinking water) two-generation reproductive toxicity study of dibromoacetic acid (DBA) in rats

In a two-generation study of dibromoacetic acid (DBA), Crl SD rats (30 rats/sex/group/generation) were provided DBA in drinking water at 0 (reverse osmosis-deionized water), 50, 250, and 650 ppm (0, 4.4 to 11.6, 22.4 to 55.6, and 52.4 to 132.0 mg/kg/day, respectively; human intake approximates 0.1 microg/kg/day [0.0001 mg/kg/day]). Observations included viability, clinical signs, water and feed consumption, body and organ weights, histopathology, and reproductive parameters (mating, fertility, abortions, premature deliveries, durations of gestation, litter sizes, sex ratios and viabilities, maternal behaviors, reproductive organ weights, sperm parameters and implantation sites, sexual maturation). Histopathological evaluations were performed on at least 10 P and F1 rats/sex at 0 and 650 ppm (gross lesions, testes, intact epididymis; 10 F1 dams at 0, 250, and 650 ppm for primordial follicles). Developmental observations included implantations, pup numbers, sexes, viabilities, body weights, morphology, and reproductive performance. At 50 ppm and higher, both sexes and generations had increased absolute and relative liver and kidneys weights, and female rats in both generations had reduced absolute and relative adrenal weights; adrenal changes were probably associated with physiological changes in water balance. The livers and kidneys (10/sex/group/generation) had no histopathological changes. Other minimal effects at 50 ppm were reduced water consumption and a transient reduction in body weight. At 250 and 650 ppm, DBA reduced parental water consumption, body weight gains, body weights, feed consumption, and pup body weights. P and F1 generation male rats at 250 and 650 ppm had altered sperm production (retained step 19 spermatids in stages IX and X tubules sometimes associated with residual bodies) and some epididymal tubule changes (increased amounts of exfoliated spermatogenic cells/residual bodies in epididymal tubules, atrophy, and hypospermia), although inconsistently and at much lower incidences. Unilateral abnormalities of the epididymis (small or absent epididymis) at 650 ppm in four F1 generation male rats were considered reproductive tract malformations. The no-observable-adverse-effect level (NOAEL) and reproductive and developmental NOAELs for DBA were at least 50 ppm (4.5 to 11.6 mg/kg/day), 45,000 to 116,000 times the human adult exposure level. Reproductive and developmental effects did not occur in female rats exposed to DBA concentrations as high as 650 ppm. Based on the high multiples of human exposure required to produce effects in male rats, DBA should not be identified as a human reproductive or developmental risk.     

Oral (drinking water) two-generation reproductive toxicity study of bromodichloromethane (BDCM) in rats

Bromodichloromethane (BDCM) was tested for reproductive toxicity in a two-generation study in CRL SD rats. Thirty rats/sex/ group/generation were continuously provided BDCM in drinking water at 0 (control carrier, reverse osmosis membrane-processed water), 50,150, and 450 ppm (0, 4.1 to 12.6, 11.6 to 40.2, and 29.5 to 109.0 mg/kg/day, respectively). Adult human intake approximates 0.8 microg/kg/day (0.0008 mg/kg/day). P and F1 rats were observed for general toxicity (viability, clinical signs, water and feed consumption, body weights, organ weights [also three weanling Fl and F2 pups/sex/litter], histopathology [10/sex, 0- and 450-ppm exposure groups]) and reproduction (mating, fertility, abortions, premature deliveries, durations of gestation, litter sizes, sex ratios, viabilities, maternal behaviors, reproductive organ weights [also three weanling Fl and F2 pups/sex/ litter], sperm parameters, and implantations. F1 rats were evaluated for age at vaginal patency or preputial separation. Ten P and F1 rats/sex from the 0- and 450-ppm exposure groups and rats at 50 and 150 ppm with reduced fertility were evaluated for histopathology (gross lesions, testes, intact epididymis, all F1 dams for number of primordial follicles). Developmental parameters in offspring included implantation and pup numbers, sexes, viabilities, body weights, gross external alterations, and reproductive parameters (Fl adults). Toxicologically important, statistically significant effects at 150 and/or 450 ppm included mortality and clinical signs associated with reduced absolute and relative water consumption, reduced body weights and weight gains, and reduced absolute and relative feed consumption (P and F1 rats). Significantly reduced body weights at 150 and 450 ppm were associated with reduced organ weights and increased organ weight ratios (% body and/or brain weight). Histopathology did not identify abnormalities. Small delays in sexual maturation (preputial separation, vaginal patency) and more Fl rats with prolonged diestrus were also attributable to severely reduced pup body weights. Mating, fertility, sperm parameters, and primordial ovarian follicular counts were unaffected. The no-observable-adverse-effect level (NOAEL) and the reproductive and developmental NOAELs for BDCM were at least 50 ppm (4.1 to 12.6 mg/kg/day), 5125 to 15,750 times the human adult exposure level, if delayed sexual maturational associated with severely reduced body weights is considered reproductive toxicity. If considered general toxicity, reproductive and developmental NOAELs for BDCM are greater than 450 ppm (29.5 to 109.0 mg/kg/day), or 36,875 to 136,250 times the human adult exposure level. Regardless, these data indicate that BDCM should not be identified as a risk to human reproductive performance or development of human conceptuses.     

Two-Generation Reproductive Toxicity Study of Dietary Tributyl Phosphate in CD Rats

Tributyl phosphate (TBP) was tested for reproductive toxicityin rats. Thirty weanlings/sex (F0) were exposed to TBP in thediet ad libitum at 0, 200, 700, or 3000 ppm for 10 weeks andthen randomly mated within groups for 3 weeks with continuedexposure. F0 parents and 10 F1 weanlings/sex/dose were necropsied,and adult reproductive organs, urinary bladders (both sexes),kidneys (males), and livers (females) were evaluated histologically.Thirty F1 weanlings/sex/dose continued exposure for 11 weeksand were bred as described above. F1 parents and P2 weanlings,10/sex/dose, were then necropsied as described above. Adulttoxicity was observed in both sexes and generations at 700 and3000 ppm; observations included reduced body weights, weightgain and feed consumption, urinary bladder epithelial hyperplasia(both sexes), renal pelvis epithelial hyperplasia only at 3000ppm (male kidneys), and centrilobular hypertrophy (female livers).At 200 ppm, transient reductions in body weight were observedin F0 and F1 females, with urinary bladder epithelial hyperplasiain F0 males and females and in F1 males. There was no evidenceof reproductive toxicity, of reproductive organ pathology, orof effects on gestation or lactation at any dose tested. Postnataltoxicity was evidenced by consistent reductions in F1 and F2pup body weights at 3000 ppm and by occasional weight reductionsin F2 litters at 700 ppm, and was associated with maternal toxicityobserved at these doses and times. Under the conditions of thisstudy, a NOAEL was not determined for adult toxicity; the NOAELfor reproductive toxicity was at least 3000 ppm and the NOAELfor postnatal toxicity was approximately 200 ppm.     

Inhalation two-generation reproductive toxicity study of methyl isobutyl ketone in rats

To evaluate whether methyl isobutyl ketone (MIBK) affects reproductive performance, a two-generation reproduction study was conducted. MIBK was administered to 30 Sprague-Dawley rats/sex/group via whole-body inhalation at concentrations of 0, 500, 1000, or 2000 ppm, 6 h daily, for 70 days prior to mating. F(0) and F(1) females were exposed from mating through gestation day 20 and from postnatal day 5; F(2) litters were maintained through postnatal day 21. No treatment-related mortality of adult animals occurred. There was a dose-related increase in adult animals with no or a decreased response to a sound stimulus at 1000 and 2000 ppm; however, no adverse clinical signs occurred 1 h after exposure, suggesting this was a transient sedative effect. Clinical signs of central nervous system (CNS) depression in the pups were observed and one F(1) pup died after initial exposure to 2000 ppm on postnatal day 22; subsequently exposure was delayed until postnatal day 28. Decreased body weight gain and slight decreased food consumption were observed during the first 2 weeks of exposure in both generations at 2000 ppm. There were no adverse effects on male and female reproductive function or landmarks of sexual maturation. Increased F(0) and F(1) liver weights with associated centrilobular hypertrophy occurred in rats at 2000 ppm, indicative of an adaptive response. Increased male kidney weights at all exposure concentrations, associated with hyaline droplets, were indicative of male rat-specific nephropathy. Other than acute sedative effects, the no-observed-adverse-effect level (NOAEL) for parental systemic effects (excluding male rat kidney) was 1000 ppm, based on transient decreased body weight and food consumption; for reproductive effects, 2000 ppm, the highest concentration tested; and for neonatal toxicity, 1000 ppm (based on acute CNS depressive effects).     

A two-generation reproductive toxicity study of decamethylcyclopentasiloxane (D5) in rats exposed by whole-body vapor inhalation

This two-generation reproduction study assessed the reproductive hazard potential of decamethylcyclopentasiloxane (D(5)). Sprague-Dawley rats (30/sex/group) were exposed by whole-body vapor inhalation to a target concentration of 30, 70, or 160 ppm D(5) or filtered air for 6h/day. Exposures for the F(0) and F(1) generations started at least 70 days prior to mating and lasted through weaning of the respective pups on postnatal day (PND) 21. Female exposures were interrupted from gestation day (GD) 21 through PND 4 to allow for parturition and to permit continuous maternal care for the early neonates. F(2) pups were not directly exposed to D(5). There were no exposure-related mortalities, clinical signs of toxicity, or effects on body weight or food consumption. There were no treatment-related gross findings or organ weight effects at the F(0) and F(1) necropsies. Other than minimal alveolar histiocytosis in all exposed groups, there were no noteworthy microscopic findings. Reproductive parameters (number of days between pairing and mating, mating and fertility indices, gestation length, and parturition), spermatogenic parameters and ovarian primordial follicle counts and numbers of corpora lutea in the F(0) and F(1) parental animals were not significantly changed between treated and control groups. Mean live litter sizes, number of pups born, sex ratios, pup body weights, postnatal pup survival and general physical condition of offspring in each generation were not affected. The slight, but statistically significant, increase in the mean F(1) male pup AGD in the 160 ppm group was not considered to be related to treatment. Vaginal patency and balanopreputial separation were unchanged compared to controls. Thus, the No-Observed-Adverse-Effect-Level (NOAEL) for parental and reproductive toxicity was determined to be 160 ppm D(5).     

Three-Generation Reproduction Study with Dioctyl Sodium Sulfosuccinate in Rats

Three-Generation Reproduction Study with Dioctyl Sodium Sulfosuccinatein Rats. MACKENZIE, K., HENWOOD, S., FOSTER, G., AKIN, F., DAViS,R., DEBAECKE, P., SISSON, G., AND MCKINNEY, G. (1990). Fundam.Appl Toxicol. 15, 53–62. Groups of 30 male and 30 femalerats (F0) were fed diets containing 0, 0. 1, 0.5, or 1.0% dioctylsodium sulfosuccinate (DSS) for 10 and 2 weeks, respectively.The F0 animals were then mated to produce an F1 litter. Groupsof 30 male and 30 female F1 animals were fed the same dose levelsfor at least 10 weeks postweaning, and the breeding programwas repeated to produce F2 animals. F3 animals were producedfrom F2 animals by the same procedure. The study was terminatedwith the F3 wean lings. Test diets were fed continuously throughoutthe study. All F0, F1, and F2 adults and F3 weanlings (one/sex/litter)were necropsied and given a macroscopic examination. There wereno effects on reproductive function for parental animals ofeither sex during any of the three generations in this study.At the highest dose level (1.0% DSS), body weights were lowerthan those of controls dunng the premating phase for males inall three generations and for F1 and F2 females. Body weightsfor F1 and F2 males and females in the 0.5% dose group werealso low during the premating phase. Pup weights on LactationDay 0 were significantly lower than those of controls only forthe high-dose group during the third generation. However, lowerpup weight gains in the mid-and high-dose groups resulted insignificantly lower pup weights on Day 21 for all three generations.Perinatal pup survival across three generations ranged from96 to 100% for the control and treated groups. Pup survivalranged from 95 to 100% for controls, from 98 to 100% for low-and mid-dose groups, and from 91 to 99% for the high-dose group.There were no treatment-related mortality and antemortem ormacroscopic observations. In summary, DSS administered in thediet to three successive generations of rats at levels of 0.5and 1.0% caused a reduction in body weights for parental malesin all generations and for F1 and F2 females, Pup weights atthe 0.5 and 1.0% dose levels were also lower than those of thecontrol in all three generations. However, the reduced bodyweights did not interfere with development of normal reproductiveperformance. DSS at levels up to 1.0% had no effects on thereproductive function of either sex in any generation and producedno treatment-related antemortem or macroscopic observations.     

A two generation reproductive toxicity study with curcumin, turmeric yellow, in Wistar rats.

The reproductive toxicity of curcumin, turmeric yellow, in Wistar rats was studied in order to generate additional relevant toxicity information for the use of curcumin in humans by oral administration. The two generation reproduction study was designed and conducted in accordance with OECD Guideline No. 416 [OECD, 1983. Guidelines for Testing of Chemicals, Guideline No. 416. Two Generation Reproduction Toxicity Study, adopted on 26th May 1983] and in compliance with Good Laboratory Practices (OECD, 1997 Principles of Good Laboratory Practice for the Testing of Chemicals. OECD, C(97)186/Final). The curcumin, mixed in the experimental diet at the concentrations of 1500, 3000 and 10,000 ppm was fed to three groups of rats, i.e., low, mid and high dose groups, and studied for two successive generations. A concurrent control group received experimental diet without the curcumin mixture. There were no treatment related adverse toxicological effects in the parental animals. No gross or microscopic changes were observed in any of the organs. None of the reproductive parameters were affected and there were no effects on the offspring other than a small reduction in pre-weaning body weight gain of the F2 pups at the highest dose level. It was concluded that the no observed adverse effect level (NOAEL) for reproductive toxicity of curcumin, fed in the diet for two successive generations to rats in this study was 10,000 ppm, which is equivalent to 847 and 959 mg/kg bodyweight (bw) per day for male rats and 1043 and 1076 for females for F0 and F1 generations, respectively. This study was the final toxicology study on curcumin reviewed by the Joint FAO/WHO Expert Committee on Food Additives (JECFA) at the 61st Meeting, 2003. The JECFA group considered that the small body weight reduction in the F2 pups of the highest dose group prevented this from being regarded as a no adverse effect level, and so allocated an ADI for curcumin of 0-3 mg/kg bw based on the intake of 250-320 mg/kg bw in the mid-dose group as the NOEL.     

A limited three-generation reproduction study on hexachlorocyclohexane (HCH) in rats.

Dietary feeding of technical hexachlorocyclohexane (HCH) at 125 and 250 ppm to rats have not shown any adverse effects on reproductive function and were comparable to control animals in a three-generation study. There were no major malformations, while some minor variants found were not compound or dose related. Despite some mild toxicological effects in rats of the P(0) generation, the litters of F(1B), F(2B) and F(3B) generations were devoid of any morphological or teratological changes. The presence of HCH residues in vital tissues of F(3B) pups have indicated transmigration of HCH in preceding generations but not to an extent that produced adverse effects.     

Chronic dietary toxicity and oncogenicity evaluation of MCPA (4-chloro-2-methylphenoxyacetic acid) in rodents

The chronic toxicity and oncogenicity of 4-chloro-2-methylphenoxyacetic acid (MCPA) were evaluated in Wistar rats at target doses of 20, 80, and 320 ppm for 2 years. Chronic effects were noted in male and/or female rats in the 80- and 320-ppm dose groups, namely elevations in triglycerides and serum glutamic transaminase levels. Nephrotoxicity was confined to male rats in the 320-ppm dose group. The systemic NOEL was determined to be 20 ppm for male and female rats. No oncogenic potential was observed. Doses in the 2-year oncogenicity study in mice were 20, 100, and 500 ppm. Kidney weight changes with corresponding minor histopathological findings in the kidney were evident in females in the 500-ppm dose group. MCPA was determined to have no oncogenic potential in B6C3F1 mice. In summary, there is no evidence of any oncogenic potential after dietary exposure of MCPA in rats or mice even at doses where limited chronic toxicity is seen.     

Two-generation reproduction study and immunotoxicity screen in rats dosed with phenol via the drinking water

This study evaluated the potential reproductive toxicity of phenol in a rat two-generation reproduction study, which included additional study endpoints, such as sperm count and motility, developmental landmarks, histological evaluation of suspect target organs (liver, kidneys, spleen, and thymus), weanling reproductive organ weights, and an immunotoxicity screening plaque assay. Phenol was administered to 30 Sprague-Dawley rats/sex/group in the drinking water at concentrations of 0, 200, 1000, or 5000 ppm. Parental (P1) animals were treated for 10 weeks prior to mating, during mating, gestation, lactation, and until sacrifice. The F1 generation (P1 offspring) was treated using a similar regimen, while the F2 generation was not treated. After mating, 10 P1 males/group were evaluated using standard clinical pathology parameters and an immunotoxicity screening plaque assay. Significant reductions in water and food consumption were observed in the 5000-ppm group in both generations; corollary reductions in body weight/body weight gain were also observed. Mating performance and fertility in both generations were similar to controls, and no adverse effects on vaginal cytology or male reproductive function were observed. Vaginal opening and preputial separation were delayed in the 5000-ppm group, and were considered to be secondary to the reduction in F1 body weight. Litter survival of both generations was reduced in the 5000-ppm group. Absolute uterus and prostate weights were decreased in the F1 generation at all dose levels; however, no underlying pathology was observed and there was no functional deficit in reproductive performance. Therefore, these findings were not considered to be adverse. No evidence of immunotoxicity was noted in the 5000-ppm group. The effects noted at the high concentration were presumed to be associated with flavor aversion to phenol in the drinking water. Based on a comprehensive examination of all parameters, the no-observable-adverse-effect level (NOAEL) for reproductive toxicity of phenol administered in drinking water to rats is 1000 ppm. The corresponding daily intake of phenol for an adult rat at the NOAEL of 1000 ppm is equivalent to about 70 mg/kg/day for males and 93 mg/kg/day for females.     

1,3-Dichloropropene: Two-Generation Inhalation Reproduction Study in Fischer 344 Rats

1,3-Dichloropropene: Two-Generation Inhalation ReproductionStudy in Fischer 344 Rats. BRESLIN, W. J., KIRK, H. D., STREETER,C. M., QUAST, J. F.,AND SZABO, J. R. (1989). Fundam. Appl Toxicol.12, 129–143. This study evaluated the effects of inhaledtechnical-grade 1,3-dichloropropene (DCPT) on reproduction andneonatal growth and survival. Groups of 30 male and 30 femaleFischer 344 rats, approximately 6 weeks of age, were exposedvia inhalation to 0, 10, 30 or 90 ppm DCPT for 6 hr/day, 5 days/week,for two generations. The parental f₀ and f₁ generations wereeach bred twice. Reproductive and neonatal parameters evaluatedincluded indices of fertility and pup survival, gestation length,litter size, pup body weight, and pup sex ratio. Gross and histologicexaminations were conducted on all f₀ and f₁ adults. In addition,randomly selected f_1b and f_2b weanlings were given gross examinations.Parental effects were limited to rats exposed to 90 ppm DCPTand included decreased body weights and histopathologic effectson the nasal mucosa of adult male and female rats. The histopathologiceffects consisted of slight, focal hyperplasia of the respiratoryepitheium and/or focal degenerative changes in the olfactoryepithelium. No adverse effects on reproductive parameters orneonatal growth or survival were observed in the f_1a, f_1b, f_2a,or f_2b litters even at an exposure concentration which producedeffects in adult animals. Based on these results, it is concludedthat inhalation exposure of rats up to 90 ppm DCPT for two successivegenerations did not adversely affect the reproductive and neonatalparameters evaluated.