Bisphenol A (BPA) was evaluated at concentrations of 0, 0.015, 0.3, 4.5, 75, 750, and 7500 ppm ( approximately 0.001, 0.02, 0.3, 5, 50, and 500 mg/kg/day of BPA) administered in the diet ad libitum to 30 CD((R)) Sprague-Dawley rats/sex/dose for 3 offspring generations, 1 litter/generation, through F3 adults. Adult systemic toxicity at 750 and 7500 ppm in all generations included: reduced body weights and body weight gains, reduced absolute and increased relative weanling and adult organ weights (liver, kidneys, adrenals, spleen, pituitary, and brain), and female slight/mild renal and hepatic pathology at 7500 ppm. Reproductive organ histopathology and function were unaffected. Ovarian weights as well as total pups and live pups/litter on postnatal day (PND) 0 were decreased at 7500 ppm, which exceeded the adult maximum tolerated dose (MTD). Mating, fertility, gestational indices; ovarian primordial follicle counts; estrous cyclicity; precoital interval; gestational length; offspring sex ratios; postnatal survival; nipple/areolae retention in preweanling males; epididymal sperm number, motility, morphology; daily sperm production (DSP), and efficiency of DSP were all unaffected. At 7500 ppm, vaginal patency (VP) and preputial separation (PPS) were delayed in F1, F2, and F3 offspring, associated with reduced body weights. Anogenital distance (AGD) on PND 0 was unaffected for F2 and F3 males and F3 females (F2 female AGD was increased at some doses, not at 7500 ppm, and was considered not biologically or toxicologically relevant). Adult systemic no observed adverse effect level (NOAEL) = 75 ppm (5 mg/kg/day); reproductive and postnatal NOAELs = 750 ppm (50 mg/kg/day). There were no treatment-related effects in the low-dose region (0.001-5 mg/kg/day) on any parameters and no evidence of nonmonotonic dose-response curves across generations for either sex. BPA should not be considered a selective reproductive toxicant, based on the results of this study.

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.

Melatonin (MEL) is a widely used, over-the-counter sleep aid, and it has putative contraceptive, antioxidant, antiaging, and anticancer effects. The developmental toxicity potential for repeated oral doses of MEL had not previously been evaluated. In the present studies, time-mated, Sprague-Dawley-derived (CD) rats were administered MEL or vehicle by gavage on gestation days (gd) 6-19. MEL-treated groups received 1-, 10-, 100-, 150-, or 200-mg/kg body weight/day in the screening study (15 rats/group), and 50, 100, or 200 mg/kg/day in the definitive study (25 rats/group). In both studies, maternal food/water consumption, body weight, and clinical signs were monitored at regular intervals throughout gestation. At termination (gd 20, both studies), maternal liver and gravid uterine weights, number of ovarian corpora lutea, conceptus survival, fetal sex, and fetal body weight were evaluated. Fetal morphological examination included external structures (both studies) as well as visceral and skeletal structures (definitive study). In the screening study, maternal serum levels of 17beta-estradiol, progesterone, prolactin, and luteinizing hormone were determined by radioimmunoassay, and mammary tissue was fixed, stained, and evaluated for percent glandular area within the fat pad. No maternal morbidity/mortality was found in either study. In the screening study, aversion to treatment (> or =100 mg/kg/day) and reduced maternal weight gain (> or =150 mg/kg/day) were noted, but reproductive/endocrine parameters and fetal development were not affected. In the definitive study, aversion to treatment was noted at > or =50 mg/kg/day, and mild sedation, reduced maternal food intake, and reduced body weight gain were found during initial treatment with 200 mg/kg/day. MEL had no effect on prenatal survival, fetal body weight, or incidences of fetal malformations/variations. Thus, in the definitive study, the maternal toxicity NOAEL and LOAEL were 100 and 200 mg/kg/day, respectively, and the developmental toxicity NOAEL was > or =200 mg/kg/day.

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