Two-generation reproductive toxicity study of dietary bisphenol A in CD-1 (Swiss) mice.

Dietary bisphenol A (BPA) was evaluated in a mouse two-generation study at 0, 0.018, 0.18, 1.8, 30, 300, or 3500 ppm (0, 0.003, 0.03, 0.3, 5, 50, or 600 mg BPA/kg/day, 28 per sex per group). A concurrent positive control group of dietary 17beta-estradiol (0.5 ppm; 28 per sex) confirmed the sensitivity of CD-1 mice to an endogenous estrogen. There were no BPA-related effects on adult mating, fertility or gestational indices, ovarian primordial follicle counts, estrous cyclicity, precoital interval, offspring sex ratios or postnatal survival, sperm parameters or reproductive organ weights or histopathology (including the testes and prostate). Adult systemic effects: at 300 ppm, only centrilobular hepatocyte hypertrophy; at 3500 ppm, reduced body weight, increased kidney and liver weights, centrilobular hepatocyte hypertrophy, and renal nephropathy in males. At 3500 ppm, BPA also reduced F1/F2 weanling body weight, reduced weanling spleen and testes weights (with seminiferous tubule hypoplasia), slightly delayed preputial separation (PPS), and apparently increased the incidence of treatment-related, undescended testes only in weanlings, which did not result in adverse effects on adult reproductive structures or functions; this last finding is considered a developmental delay in the normal process of testes descent. It is likely that these transient effects were secondary to (and caused by) systemic toxicity. Gestational length was increased by 0.3 days in F1/F2 generations; the toxicological significance, if any, of this marginal difference is unknown. At lower doses (0.018-30 ppm), there were no treatment-related effects and no evidence of nonmonotonic dose-response curves for any parameter. The systemic no observable effect level (NOEL) was 30 ppm BPA (approximately 5 mg/kg/day); the reproductive/developmental NOEL was 300 ppm (approximately 50 mg/kg/day). Therefore, BPA is not considered a selective reproductive or developmental toxicant in mice.

One-generation reproductive toxicity study of dietary 17beta-estradiol (E2; CAS No. 50-28-2) in CD-1 (Swiss) mice.

There is no information on reproductive/developmental effects in mice from dietary estrogen. Therefore, 10 adult CD-1 mice/sex/group were administered dietary 17beta-estradiol (E2) at 0, 0.005, 0.05, 0.5, 2.5, 5, 10, and 50 ppm for 2-week prebreed, mating, gestation, lactation. F1 weanlings (3/sex/litter) were necropsied and 2/sex/litter were retained, with exposure, until vaginal patency (VP) or preputial separation (PPS) and then necropsied. Results included complete infertility at 2.5-50 ppm with normal mating indices. At 0.5 ppm (and above), F0 adult female uterus plus cervix plus vagina weights (UCVW) were increased. At 0.5 ppm: prolonged gestational length; increased F1 stillbirth index; reduced live birth index and litter size; decreased testes and epididymides weights at weaning; unaffected AGD on pnd 0 and 21; delayed PPS; increased undescended testes; unaffected prostate weight; accelerated VP; enlarged vaginas; fluid-filled uteri. At 0.05 ppm: no F0 reproductive effects, increased F1 weanling UCVW; delayed PPS. The NOEL was 0.005 ppm ( approximately 1 microg/kg/day).

Two-generation reproductive toxicity evaluation of dietary 17beta-estradiol (E2; CAS No. 50-28-2) in CD-1 (Swiss) mice.

No information exists on reproductive/developmental effects in mice exposed to dietary 17beta-estradiol (E2) over multiple generations. Therefore, under OECD Test Guideline 416 with enhancements, CD-1 mice (F0 generation, 25 mice/sex/group) were exposed to dietary E2 at 0, 0.001, 0.005, 0.05, 0.15, or 0.5 ppm ( approximately 0, 0.2, 1, 10, 30, or 100 mug E2/kg body weight/day) for 8 weeks prebreed, 2 weeks mating, approximately 3 weeks gestation, and 3 weeks lactation. At weaning, selected F1 offspring (F1 parents; 25/sex/group) and extra retained F1 males (one per litter) were exposed to the same dietary concentrations and durations as the F0 generation; study termination occurred at F2 weaning; F1/F2 weanlings (up to three per sex per litter) were necropsied with organs weighed. At 0.5 ppm, effects were increased F1/F2 perinatal loss, prolonged F0/F1 gestational length, reduced numbers of F2 (but not F1) litters/group, reduced F1/F2 litter sizes, accelerated vaginal patency (VP) and delayed preputial separation (PPS), increased uterus + cervix + vagina weights (UCVW) in F0/F1 adults and F1/F2 weanlings, and decreased testes and epididymides weights (TEW) in F1/F2 weanlings. At 0.15 ppm, effects were increased UCVW in F0/F1 adults and F1/F2 weanlings, accelerated VP, delayed PPS, and reduced TEW in F1/F2 weanlings. At 0.05 ppm, UCVW were increased in F1/F2 weanlings, and PPS was delayed only in extra retained F1 males. There were no biologically significant or treatment-related effects on F0/F1 parental body weights, feed consumption, or clinical observations, or on F0/F1 estrous cyclicity, F0/F1 andrology, or F1/F2 anogenital distance at any dose. The no observable effect level was 0.005 ppm E2 ( approximately 1 mug/kg/day). Therefore, the mouse model is sensitive to E2 by oral administration, with effects on reproductive development at doses of 10- 100 mug/kg/day.

Three-generation evaluation of dietary para-nonylphenol in CD (Sprague-Dawley) rats.

This study evaluated the potential for dietary para-nonylphenol (NP; CAS No. 84852-15-3) to affect parental fertility and growth and development of three offspring generations in CD (Sprague-Dawley [SD]) rats, including sperm counts across generations to determine the validity of equivocal reductions observed in the F2 generation by R. E. Chapin et al. (1999, Toxicol. Sci. 52, 80-91). Male rat kidney toxicity was also examined based on inconsistent observations in NP-exposed rats at 2000 ppm but not at 200 or 650 ppm in Purina 5002 (H. C. Cunny et al., 1997, Regul. Toxicol. Pharmacol. 26, 172-178) and at all of these NP concentrations in NIH-07 diet (R. E. Chapin et al., 1999, Toxicol. Sci. 52, 80-91). Concentrations were 0, 20, 200, 650, and 2000 ppm NP in Purina 5002 diet and 0 and 650 ppm NP in NIH-07 diet. 17beta-estradiol (E2) was used as a positive control at 2.5 ppm in Purina 5002 diet. There were no NP effects on any reproductive parameters in any generation, including sperm counts. Kidney toxicity (histopathology) occurred at 650 and 2000 ppm with no clear difference for the two diets. Ovarian weight was decreased at 2000 ppm NP in all generations, with no effect on reproduction. Dietary E2 at 2.5 ppm caused renal, reproductive, and developmental (lactational and peripubertal) toxicity in all generations. This study confirmed that dietary NP is not a selective reproductive toxicant with an no observable adverse effect level (NOAEL) of > 2000 ppm ( approximately > 150 mg/kg/day) and provided an NOAEL for male rat kidney toxicity of 200 ppm NP (approximately 15 mg/kg/day).