Melissa C. Marr

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.

The Developmental Toxicity of Bisphenol A in Rats and Mice

Bisphenol A (BPA) was evaluated for developmental toxicity in CD rats (0, 160, 320, or 640 mg/kg/day) and CD-1 mice (0, 500, 750, 1000, or 1250 mg/kg/day) dosed daily by gastric intubation on Gestational Days 6 through 15. Timed-pregnant dams were sacrificed 1 day prior to parturition, the uterine contents were examined, and all fetuses were examined for external, visceral, and skeletal malformations. In rats, maternal weight gain during gestation, weight gain corrected for gravid uterine weight, and weight gain during treatment were significantly reduced at all BPA doses. Gravid uterine weight and average fetal body weight per litter were not affected by BPA. No increase in percentage resorptions per litter or percentage fetuses malformed per litter was detected. In mice, maternal mortality occurred at all BPA doses, reaching 18% at the high dose, which also produced a significant decrease in maternal body weight gain during gestation and treatment. Weight gain corrected for gravid uterine weight was not affected by BPA. Reductions in gravid uterine weight and average fetal body weight were observed with the 1250 mg/kg dose of BPA. Relative maternal liver weight was increased at all doses of BPA. There was a significant increase in the percentage of resorptions per litter with 1250 mg BPA/kg/day. Malformation incidence was not altered by BPA. Thus, BPA treatment at maternally toxic dose levels during organogenesis produced fetal toxicity in mice but not in rats and did not alter fetal morphologic development in either species.

The developmental toxicity of ethylene glycol in rats and mice

Timed-pregnant CD rats and CD-1 mice were dosed by gavage with ethylene glycol (EG) in distilled water on gestational days (gd) 6 through 15 (0, 1250, 2500, or 5000 mg kg-1 day-1 for rats; and 0, 750, 1500, or 3000 mg kg-1 day-1 for mice). Females were observed daily during treatment, but no maternal deaths or distinctive clinical signs were noted. Dose-related decreases in maternal weight gain during treatment were significant at all doses in rats and at the mid and high doses in mice. Gravid uterine weight was reduced in both species at the mid and high doses, and corrected maternal gestational weight gain showed a significant decreasing trend. At termination (gd 20, rats; gd 17, mice), the status of uterine implantation sites was recorded, and live fetuses were weighed and examined for external, visceral, and skeletal malformations. Dose-related increases in postimplantation loss per litter were observed in both species with the high dose significantly above controls only in rats. Fetal body weight per litter was significantly reduced at the mid and high doses in rats and at all doses in mice. The percentage of malformed live fetuses per litter and/or the percentage of litters with malformed fetuses was significantly elevated in all EG dose groups and greater than 95% of litters were affected at the high dose for each species. A wide variety of malformations were observed; the most common in both species were craniofacial and neural tube closure defects and axial skeletal dysplasia. EG produced severe developmental toxicity in two rodent species at doses that apparently failed to produce any serious maternal effects.

Developmental Toxicity Evaluation of Dietary Di(2-ethylhexyl) phthalate in Fischer 344 Rats and CD-1 Mice

Di(2-ethylhexyl)phthalate (DEHP), a widely used plasticizing agent, was evaluated for developmental toxicity in timed-pregnant Fischer 344 rats (22-25 dams/dose) and CD-1 mice (24-30 dams/dose). DEHP was administered in the diet on gestational Days (gd) 0 through 20 at 0.0, 0.5, 1.0, 1.5, or 2.0% (rats) and on gd 0 through 17 at 0.00, 0.025, 0.05, 0.10, or 0.15% (mice). At termination (gd 20, rats; gd 17 mice), all fetuses were examined for external, visceral, and skeletal malformations and variations. In rats, maternal toxicity and reduced fetal body weight per litter were observed at 1.0, 1.5, and 2.0%. Increased resorptions and decreased number of live fetuses/litter were observed at 2.0%. Maternal food consumption was reduced and water consumption was increased in all DEHP groups. The number and percentage of fetuses malformed per litter were unaffected by treatment. In mice, maternal toxicity, increased resorptions and late fetal deaths, decreased number of live fetuses, and reduced fetal body weight per litter were observed at 0.10 and 0.15%. Maternal food and water consumption exhibited a dose-related upward trend with food consumption significantly increased at 0.15%. The number and percentage of fetuses malformed per litter (open eye, exophthalmia, exencephaly, short, constricted, or no tail, major vessel malformations, fused or branched ribs, and fused or misaligned thoracic vertebral centra) were elevated at 0.05, 0.10, and 0.15% DEHP. In conclusion, DEHP was not teratogenic at any dose tested in Fischer 344 rats when administered in the feed throughout gestation but did produce maternal and other embryofetal toxicity at 1.0, 1.5, and 2.0%. In contrast, DEHP administration throughout gestation in CD-1 mice resulted in an increased incidence of malformations at doses which produced maternal and other embryofetal toxicity (0.10 and 0.15%) and at a dose (0.05%) which did not produce significant maternal toxicity. No treatment-related embryofetal toxicity including teratogenicity was observed in mice at 0.025% or in rats at 0.5% DEHP.

Developmental Toxicity of Boric Acid in Mice and Rats

Boric acid (BORA), an ingredient of many cosmetics, pharmaceuticals, and pesticides, was tested for developmental toxicity in timed-pregnant Swiss mice and Sprague-Dawley rats (n = 26-28/group). BORA (0, 0.1, 0.2, or 0.4% in feed) was provided throughout gestation to attain steady-state exposure as early as possible during prenatal development. Average doses (mg/kg/day) were 248, 452, or 1003 in mice, and 78, 163, or 330 in rats. To limit prenatal mortality, BORA (0.8% or 539 mg/kg/day) was provided to an additional group of rats on Gestational Days (GD) 6 to 15 only. On GD 17 (mice) or 20 (rats), fetuses were weighed and examined for malformations (external, visceral, skeletal). Mouse dams exhibited mild renal lesions (greater than or equal to 0.1%), increased water intake and relative kidney weight (0.4%), and decreased weight gain (0.4%) during treatment. There was a reduction of fetal body weight (greater than or equal to 0.2%) and an increased incidence of resorptions and malformed fetuses per litter (0.4%). Morphological changes included an increased incidence of short rib XIII (a malformation) and a decreased incidence of rudimentary or full rib(s) at lumbar I (an anatomical variation). Maternal rats exhibited increased liver and kidney weights at greater than or equal to 0.2%, altered water and/or food intake at greater than 0.2%, and decreased weight gain at greater than 0.4%. Average fetal body weight/litter was reduced at all doses. Prenatal mortality was increased only at 0.8%. The incidence of fetal malformations was significantly increased at greater than or equal to 0.2%. The most frequently observed malformations were enlarged lateral ventricles of the brain and agenesis or shortening of rib XIII. In rats, the no-observable-adverse-effect level (NOAEL) for maternal toxicity was 78 mg/kg (0.1%), while in mice the low dose of 248 mg/kg (0.1%) approached the maternal NOAEL with mild renal lesions in only 2 of 10 females. Embryo/fetal toxicity occurred in all groups of rats at greater than or equal to 78 mg/kg (greater than or equal to 0.1%) while the NOAEL for developmental toxicity in mice was 248 mg/kg (0.1%). Thus developmental toxicity occurred below maternally toxic levels in rats as well as in the presence of maternal toxicity in mice and rats.

Relationship between acrylamide reproductive and neurotoxicity in male rats

To determine whether there is a relationship between the reproductive and neurotoxic effects of acrylamide monomer (AM), the first week of the study design of Sublet et al. ¿14 was duplicated: Long-Evans male rats were gavaged with AM in water, 25/group, at 0, 5, 15, 30, 45, or 60 mg/kg/day for 5 days (days 1 through 5). On Day 8, males were paired overnight with untreated virgin females (1 : 1) in proestrus/estrus. On day 9, males were evaluated for forelimb and hindlimb grip strength. Five males/group were perfusion fixed, 20/group were used for andrologic assessment, and all were necropsied. Perfusion-fixed sciatic nerves were examined histologically. Sperm-positive females were examined for preimplantation and postimplantation loss at midpregnancy. At 15 to 60 mg/kg/day, males exhibited significantly reduced weight gain, reduced mating, fertility, and pregnancy indices by trend analysis (significant at 60 mg/kg/d by pairwise comparison), and increased postimplantation loss and dominant lethal factor, F(L)%, at 45 and 60 mg/kg/day. At 60 mg/kg/day, the sperm beat cross frequency was increased, with no significant effects on epididymal sperm motility or concentration, and hindlimb grip strength was decreased, with no pathologic lesions in sciatic nerves. Therefore, epididymal sperm, mating, and neurotoxic effects were observed at AM doses that also resulted in increased postimplantation loss, possibly by different mechanisms.

Effects of lactational administration of acrylamide on rat dams and offspring

We duplicated the study design of Husain et al. (Ind Health 1987; 25:19-28) to determine whether maternal exposure to acrylamide monomer (AM) resulted in offspring neurotoxicity. Wistar rat dams with litters (15/group) were gavaged with AM in saline at 0 or 25.0 mg/kg/d throughout lactation (pnd 0-21). Maternal feed and water consumption, body weights (BW), and Functional Observational Battery (FOB) were recorded. At weaning (pnd 21), maternal sciatic nerves were examined histologically. Male offspring were retained until pnd 91, with BW and grip strength evaluations. Dosed dams exhibited progressive toxicity, including mortality (two), severely reduced feed and water consumption, BW, and BW gain, and behavioral neurotoxicity (with no sciatic nerve pathology). Nursing offspring at 25.0 mg/kg/d exhibited increased mortality and reduced BW associated with little/no milk in stomachs. Postwean males at 25.0 mg/kg/d exhibited normal BW gain and increasing grip strength over time. Therefore, AM caused maternal toxicity; offspring effects during lactation were consistent with inanition from maternal toxicity. Postwean males exhibited recovery with no signs of AM-mediated toxicity. These results do not support the conclusions of Husain et al.

Codeine: Developmental Toxicity in Hamsters and Mice

Timed-pregnant LVG Syrian hamsters and Swiss CD-1 mice were dosed orally twice daily (b.i.d.) with codeine in water on Gestational Days (gd) 5-13 (0, 10, 50, or 150 mg/kg, b.i.d.--hamsters) or 6-15 (0, 37.5, 75, 150, or 300 mg/kg, b.i.d.--mice). Dams were necropsied on gd 14 (hamsters) or 17 (mice), and fetuses were weighed, sexed, and examined for external, visceral, and skeletal malformations. No maternal deaths were observed in hamsters, while 19% of the pregnant mice in the high-dose group died. Maternal weight gain (gestational and treatment periods) and gravid uterine weights were significantly depressed in hamsters (150 mg/kg, b.i.d.) and in mice (300 mg/kg, b.i.d.). However, the corrected weight gain for both species, although decreased, was not significantly different from that of the controls. In both species, maternal liver weights (relative) were significantly increased in the high-dose groups. There were increases in the percentage resorptions per pregnant dam and in the proportion of litters with 100% resorptions in the high-dose groups of both species. Considering only live litters, the number of live fetuses per litter and the sex ratio were unaffected in both species. Mean fetal body weights were also significantly decreased in the 50 and 150 mg/kg, b.i.d. (hamsters), and the 150 and 300 mg/kg, b.i.d. (mice), groups. The no-observed-adverse-effect levels (NOAELs) for developmental toxicity were 10 (hamsters) and 75 (mice) mg/kg, b.i.d., whereas the NOAELs for maternal toxicity were 50 (hamsters) and 150 (mice) mg/kg, b.i.d. The predominant structural malformation in hamsters was meningoencephalocele (high-dose group only), affecting 3% of fetuses and 19% of litters (neither statistically significant). Codeine did not induce any increase in structural malformations in mice. Thus, codeine produced developmental toxicity (as indicated by decreased fetal body weight) at doses below those producing maternal toxicity in both hamsters and mice. In the hamster, the more sensitive species to codeine developmental toxicity, effects were observed at a total daily dose of 100 mg/kg, which is only 11 times the maximum human therapeutic oral dose.

Assessment of the reproductive and developmental toxicity of pesticide/fertilizer mixtures based on confirmed pesticide contamination in California and Iowa groundwater.

Pesticides and fertilizers, as used in modern agriculture, contribute to the overall low-level contamination of groundwater sources. In order to determine the potential of pesticide and fertilizer mixtures to produce reproductive or developmental toxicity at concentrations up to 100 x the median level found in groundwater, we prepared and studied two mixtures of pesticides and a fertilizer (ammonium nitrate). One mixture containing aldicarb, atrazine, dibromochloropropane, 1,2-dichloropropane, ethylene dibromide, and simazine plus ammonium nitrate was considered to be a representative of groundwater contamination in California (CAL). The other, containing alachlor, atrazine, cyanazine, metolachlor, metribuzin, and ammonium nitrate, simulated groundwater contamination in Iowa (IOWA). Each mixture was administered in the drinking water of either Swiss CD-1 mice during a Reproductive Assessment by Continuous Breeding study or pregnant Sprague-Dawley rats (gd 6-20) at three dose levels (1x, 10x, and 100x) where 1x was the median concentration of each pesticide component as determined in the groundwater surveys in California or Iowa. Unlike conventional toxicology studies, the purpose of this study was to evaluate the health effects of realistic human concentrations. Thus, the testing concentrations are probably well below the maximally tolerated dose. Propylene glycol was used as the solubilizer for the pesticides in drinking water formulations in both studies. In the reproductive study, neither mixture caused any clinical signs of toxicity, changes in food or water consumption, or body weight in either F0 or F1 mice at doses up to 100x the median groundwater concentrations. There were no treatment-related effects on fertility or any measures of reproductive performance of either the F0 or the F1 generation mice exposed to either CAL or IOWA at up to 100x. Similarly, measures of spermatogenesis, epididymal sperm concentration, percentage motile sperm, percentage abnormal sperm, and testicular and epididymal histology were normal. In the developmental study, CAL- or IOWA-exposed females did not exhibit any significant treatment-related clinical signs of toxicity. No adverse effects of CAL or IOWA were observed for measures of embryo/fetal toxicity, including resorptions per litter, live litter size, or fetal body weight. CAL or IOWA did not cause an increased incidence of fetal malformations or variations. In summary, administration of these pesticide/fertilizer mixtures at levels up to 100-fold greater than the median concentrations in groundwater supplies in California or Iowa did not cause any detectable reproductive (mice), general, or developmental toxicity (rats).

Developmental toxicity evaluation of acrylamide in rats and mice

Acrylamide (ACRL), a widely used industrial chemical with neurotoxic effects, was evaluated for developmental toxicity. ACRL in distilled water was administered once daily by gavage on gestational days (gd) 6-17 to mice (0, 3, 15, or 45 mg/kg) and on gd 6-20 to rats (0, 2.5, 7.5, or 15 mg/kg). Following termination (gd 17, mice; gd 20, rats) fetuses were examined for external, visceral, and skeletal malformations. Maternal toxicity during treatment was observed at the highest dose as reduced body weight gain in both species and hindlimb splaying in treated mice only. Weight gain corrected for gravid uterine weight was also reduced in rats at 7.5 and 15 mg/kg/day. Embryo/fetal toxicity was not observed in rats, but fetal weight was reduced in mice administered 45 mg/kg/day. No increase in the incidence of malformations was observed in either species; however, the incidence of variations (predominately extra rib) increased with dose. In summary, administration of ACRL during organogenesis produced maternal and developmental toxicity at 45 mg/kg/day in mice and maternal, but not developmental, toxicity at doses greater than or equal to 7.5 mg/kg/day in rats.