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Developmental toxicity of formate and formic acid in whole embryo culture: a comparative study with mouse and rat embryos.

Acute methanol (MeOH) toxicity in primates is attributed to the conversion of MeOH to formate and the resulting acidosis. MeOH has been shown to be developmentally toxic in mice and rats both in vivo and in vitro, but rodents neither accumulate formate nor develop acidosis after MeOH exposure. To further assess the potential human developmental toxicity of MeOH exposure, we evaluated the developmental effects of sodium (Na) formate and formic acid in rodent whole embryo culture (WEC). Day 9 rat embryos were cultured for 24 or 48 hours and day 8 mouse embryos were cultured for 24 hours in the presence of Na-formate or formic acid. Rat and mouse embryos exposed to either agent for 24 hours exhibited a trend toward reduced growth and development and the number of abnormalities increased at the higher concentrations. Rat embryos exposed for 48 hours to either Na-formate or formic acid showed a trend toward reduced growth and development with increasing concentration. Embryo lethality and incidence of abnormal embryos were also increased at the higher concentrations. The anomalies observed in both species after exposure to either compound were primarily open anterior and posterior neuropore with less frequent incidence of rotational defects, tail anomalies, enlarged pericardium and delayed heart development. Exposure to Na-formate or formic acid for comparable periods of time results in comparable degrees of embryotoxicity at concentrations (mMolar) at least 4-fold lower than those previously reported for methanol exposure.

Abnormalities, Drug-Induced↗

Effects of monoisoamyl meso-2,3-dimercaptosuccinate on arsenite-induced maternal and developmental toxicity in mice.

The therapeutic efficacy of monoisoamyl meso-2,3-dimercaptosuccinate (Mi-ADMS), on arsenite-induced maternal and developmental toxicity was evaluated in the pregnant mouse. Sodium arsenite (12 mg/kg) was intraperitoneally injected into Swiss mice on day 9 of gestation, whereas Mi-ADMS was given subcutaneously at 0.25, 5, 24, and 48 hr after arsenite exposure. Amelioration by Mi-ADMS of arsenite-induced maternal and embryofetal toxicity was assessed at 23.8, 47.5, and 95 mg/kg/day. Controls received 0.9% saline with or without arsenite. Cesarean sections were performed on gestation day 18. In the positive control group (treated with arsenite only), 20.8% of the pregnant animals died, whereas 37.5% of the dams were carrying completely resorbed litters. No arsenite-induced maternal lethality was seen following treatment with Mi-ADMS at 23.8, 47.5 and 95 mg/kg/day. Also, administration of the drug at these doses significantly reduced the embryolethality, as well as the incidence of some skeletal variations provoked by sodium arsenite. Although based on these findings, Mi-ADMS might be suggested as a potential antidote to prevent the arsenite-induced maternal and developmental toxicity, due to their reduced toxicity compared to Mi-ADMS, DMSA and DMPS would probably be more advisable for pregnant women exposed to arsenite.

Animals↗

Evaluation of developmental toxicity of 1-butanol given to rats in drinking water throughout pregnancy.

The objective of this study was to evaluate the developmental toxicity of 1-butanol in rats. Pregnant rats were given drinking water containing 1-butanol at 0.2%, 1.0% or 5.0% (316, 1454 or 5654 mg/kg/day) on days 0-20 of pregnancy. A significant decrease in maternal body weight gain accompanied by reduced food and water consumption was found at 5.0%. No significant increase in the incidence of pre- and postimplantation embryonic loss was observed in any groups treated with 1-butanol. Fetal weight was significantly lowered at 5.0%. Although a significant increase in the incidence of fetuses with skeletal variations and decreased degree of ossification was found at 5.0%, no increase in the incidence of fetuses with external, skeletal and internal abnormalities was detected in any groups treated with 1-butanol. The data demonstrate that 1-butanol is developmental toxic only at maternal toxic doses. No evidence for teratogenicity of 1-butanol was noted in rats. Based on the significant decreases in maternal body weight gain and fetal weight, it is concluded that the no observed adverse effect levels (NOAELs) of 1-butanol for both dams and fetuses are 1.0% (1454 mg/kg/day) in rats.

1-Butanol↗

Developmental toxicity studies in Crl:CD (SD) rats following inhalation exposure to trichloroethylene and perchloroethylene.

The potential for trichloroethylene (TCE) and perchloroethylene (PERC) to induce developmental toxicity was investigated in Crl:CD (SD) rats whole-body exposed to target concentrations of 0, 50, 150 or 600 ppm TCE or 0, 75, 250 or 600 ppm PERC for six hours/day, seven days/week on gestation day (GD) 6-20 and 6-19, respectively. Actual chamber concentrations were essentially identical to target with the exception of the low PERC exposure level, which was 65 ppm. The highest exposure levels exceeded the limit concentration (2 mg/L) specified in the applicable test guidelines. Maternal necropsies were performed the day following the last exposure. Dams exposed to 600 ppm TCE exhibited maternal toxicity, as evidenced by decreased body weight gain (22% less than control) during GD 6-9. There were no maternal effects at 50 or 150 ppm TCE and no indications of developmental toxicity (including heart defects or other terata) at any exposure level tested. Therefore, the TCE NOEC for maternal toxicity was 150 ppm, whereas the embryo/fetal NOEC was 600 ppm. Maternal responses to PERC were limited to slight, but statistically significant reductions in body weight gain and feed consumption during the first 3 days of exposure to 600 ppm, resulting in a maternal NOEC of 250 ppm. Developmental effects at 600 ppm consisted of reduced gravid uterus, placental and fetal body weights, and decreased ossification of thoracic vertebral centra. Developmental effects at 250 ppm were of minimal toxicological significance, being limited to minor decreases in fetal and placental weight. There were no developmental effects at 65 ppm.

Abnormalities, Drug-Induced↗

The developmental toxicity of inhaled methanol in the CD-1 mouse, with quantitative dose-response modeling for estimation of benchmark doses.

The developmental toxicity of the alternative motor vehicle fuel methanol was assessed in mice by the inhalation route. Pregnant CD-1 mice were exposed to 1,000, 2,000, 5,000, 7,500, 10,000, or 15,000 ppm methanol for 7 hr/day on days 6-15 of gestation. Sham-exposed controls were exposed to filtered air under similar conditions. Additional control groups were left in their home cages either unhandled or food-deprived for 7 hr/day to match the food deprivation experienced by the exposed mice. Dams were observed twice daily and weighed on alternate days during the exposure period. Blood methanol concentrations were determined in some mice on gestation days 6, 10, and 15. On day 17, the remaining mice were weighed and killed and the gravid uteri removed. Implantation sites, live and dead fetuses and resorptions were counted, fetuses were examined externally and weighed as a litter. Half of each litter was examined for skeletal morphology and the other half of each litter was examined for internal soft tissue anomalies. One dam died in each of the 7,500, 10,000, and 15,000 ppm methanol exposure groups, but no dose-response relationship was evident for maternal death. The sham-exposed and food-deprived controls as well as all methanol exposed dams gained less weight than did unexposed dams fed ad libitum, but methanol did not exacerbate this effect. Significant increases in the incidence of exencephaly and cleft palate were observed at 5,000 ppm and above, increased embryo/fetal death at 7,500 ppm and above (including an increasing incidence of full-litter resorptions), and reduced fetal weight at 10,000 ppm and above. A dose-related increase in cervical ribs or ossification sites lateral to the seventh cervical vertebra was significant at 2,000 ppm and above. Thus, the NOAEL for the developmental toxicity in this study was 1,000 ppm. A log-logistic dose response model was applied to the incidence data for exencephaly, cleft palate, resorption and cervical rib, and maximum likelihood estimates (MLEs) and benchmark dosages (BDs, the lower 95% confidence interval of the MLEs) corresponding to 1% and 5% added risk above background were calculated. The MLE for 5% added combined risk of having either exencephaly or cleft palate or being resorbed was 3667 ppm, and the corresponding BD was 3,078 ppm. For cervical rib, the 5% added risk values for the MLE and BD were 824 and 305 ppm, respectively. The BDs for 1% added risk were 1915 ppm for exencephaly, cleft palate or resorption, and 58 ppm for cervical rib.(ABSTRACT TRUNCATED AT 400 WORDS)

Abnormalities, Drug-Induced↗

Activity profiles of developmental toxicity: design considerations and pilot implementation.

The available literature was searched for quantitative test results from both in vitro and in vivo assays for developmental toxicity for five model compounds: cyclophosphamide, methotrexate, hydroxyurea, caffeine, and ethylenethiourea. These compounds were chosen on the basis of their extensive utilization in a variety of assay systems for developmental toxicity as evidenced by their representation in the ETIC database (each generally has 100-500 citations encompassing multiple test systems). Nine cellular-based assays, six assays using whole embryos in culture, as well as Segment II and abbreviated exposure tests for mammalian test species are included in the database. For each assay, the critical endpoints were identified, each of which was then provided a three-letter code, and the criteria for extraction of quantitative information were established. The extracted information was placed into a computerized reference file and subsequently plotted such that the qualitative (positive/negative) and quantitative (e.g., IC50, highest ineffective dose (HID), lowest effective dose (LED] results across all test systems could be displayed. The information contained in these profiles can be used to compare qualitative and quantitative results across multiple assay systems, to identify data gaps in the literature, to evaluate the concordance of the assays, to calculate relative potencies, and to examine structure-activity relationships.

Animals↗

Developmental toxicity of CI-921, an anilinoacridine antitumor agent.

CI-921, an anilinoacridine compound active against leukemic and solid tumors, was evaluated for potential developmental toxicity. Intravenous injections of CI-921 in dextrose were given to female Sprague-Dawley rats (0.1, 0.5, and 1.0 mg/kg) on Gestation Days (GD) 6-15 and to female New Zealand White rabbits (0.1, 1.0 and 2.0 mg/kg) on GD 6-18. Appropriate vehicle and untreated controls were included. Maternal and fetal parameters, including external, visceral, and skeletal malformations and variations, were assessed. Treatment of rats with 1.0 mg/kg resulted in maternal toxicity, manifested as reduced body weight gain and food consumption during and after treatment. Reduced fetal body weight, an increased incidence of stunted fetuses, malformations of the axial and appendicular skeleton, microphthalmia, and an increased number of anatomical variations (including anomalies of the axial skeleton and apparent hydronephrosis) also occurred in rats at 1.0 mg/kg. Treatment of rabbits resulted in no apparent maternal toxicity. However, reduced fetal body weight, agenesis of the azygous lobe of the lung, and an increased incidence of variations of the axial skeleton occurred at 2.0 mg/kg in rabbits. These results indicate that CI-921, at the highest dose tested in each species, produced developmental toxicity in the presence of maternal toxicity in rats, but in the absence of maternal toxicity in rabbits.

Abnormalities, Drug-Induced↗

Relative developmental toxicities of inhaled aliphatic mononitriles in rats.

The developmental toxicities of eight aliphatic mononitriles were studied in Sprague-Dawley rats after inhalation exposure for 6 hr/day, during Days 6 to 20 of gestation. The range of exposure concentrations for acetonitrile was 900 to 1800 ppm; for propionitrile and n-butyronitrile, 50 to 200 ppm; for isobutyronitrile, 50 to 300 ppm; for acrylonitrile and methacrylonitrile, 12 to 100 ppm; for allylnitrile 12 to 50 ppm; and for 2-chloroacrylonitrile, 1 to 12 ppm. Embryolethality was observed after exposure to 1800 ppm acetonitrile, 200 ppm propionitrile, 300 ppm isobutyronitrile; fetotoxicity was observed after exposure to 200 ppm propionitrile, n-butyronitrile, or isobutyronitrile, or to 25 ppm acrylonitrile in the presence of overt signs of maternal toxicity. In the absence of significant maternal toxicity, allylnitrile caused embryolethality, fetotoxicity, and clear teratogenicity at 50 ppm, and n-butyronitrile and methacrylonitrile caused fetotoxicity at 200 ppm and 100 ppm, respectively. While maternal toxicity was observed for 2-chloroacrylonitrile, it did not cause significant embryonal or fetal toxicity up to 12 ppm.

Acetonitriles↗

Hydroquinone: a developmental toxicity study in rats.

To determine the potential developmental toxicity of hydroquinone (HQ), pregnant rats (COBS-CD-BR) were given 0, 30, 100, or 300 mg/kg HQ by gavage on the 6th through the 15th days of gestation. Maternal effects included a slight, but significant (p less than or equal to 0.05), reduction in body weight gain and feed consumption for the 300 mg/kg HQ dams. Reproductive indices, i.e., pregnancy rate, numbers of corpora lutea, implantation sites, viable fetuses, and early and late resorptions, fetal sex ratio, pre- and postimplantation losses, and gravid uterine weights, were not affected by treatment with HQ. A slightly reduced (p less than or equal to 0.05) mean fetal body weight seen at the 300 mg/kg dose level was associated with the slightly reduced body weight gain seen for the dams at this dose level. Gross external, internal soft tissue, and skeletal examinations of the fetuses revealed no HQ-related malformations. The incidences of gross external variations (small hematomas) and internal soft tissue variations (dilated renal pelvis, hydronephrosis, and hydroureter) in the HQ-treated litters were not statistically different from the control incidences. Skeletal variations (delayed ossification of membranous skull bones, hyoid bone, thoracic centra 1-3, sacral arches 3 and 4, and bilobed thoracic centra 9-13) were seen with similar frequency in the control and HQ-treated groups. A statistically significant increase in the incidence of total common vertebral variations seen at the 300 mg/kg HQ dose level was not considered toxicologically significant. The incidences of total skeletal variations were not statistically different between the control and the HQ-treated groups.(ABSTRACT TRUNCATED AT 250 WORDS)

Abnormalities, Drug-Induced↗

Developmental toxicity studies of methyl ethyl ketoxime (MEKO) in rats and rabbits.

The developmental toxicity of methyl ethyl ketoxime (MEKO), an industrial antioxidant used primarily as an antiskinning agent in alkyd paint, was investigated in rats and rabbits. Following preliminary dose range finding studies, groups of 25 pregnant rats or 18 pregnant rabbits were dosed by gavage with aqueous solutions of MEKO at 0, 60, 200, or 600 mg/kg (rats) or 0, 8, 14, 24, or 40 mg/kg (rabbits) on gestation days 6-15 or 6-18, respectively. In rats, dose-dependent clinical signs of maternal toxicity including reduced body weight gains were noted at 200 and 600 mg/kg. At 60 mg/kg and above enlarged spleens were observed at necropsy. The preliminary study found methemoglobin formation and reticulocytosis indicative of anemia at these dose levels. No treatment-related gestational effects, malformations or developmental variations were observed in the rats. In rabbits, 3 females aborted and 8 females were found dead at 40 mg/kg between gestation days 11 and 24. Clinical signs of maternal toxicity were present in surviving doses at this dose level. Body weight gains were reduced at 24 and 40 mg/kg. The preliminary study indicated maternal hematological effects in the rabbits similar to the rats at dose levels as low as 10 mg/kg. MEKO was not considered to have produced any treatment-related gestational effects, malformations or developmental variations in the rabbit at dose levels at or below 24 mg/kg. Because of excessive maternal mortality and abortions at the 40 mg/kg dose level, only 6 rabbits produced litters. The severe maternal toxicity and limited number of litters precluded a full assessment of developmental toxicity at 40 mg/kg. Nonetheless, MEKO did not appear to be teratogenic to the rabbit at this dose level.

Abnormalities, Drug-Induced↗

Developmental toxicity evaluation of monoisoamyl meso-2,3-dimercaptosuccinate in mice.

Monoisoamyl meso-2,3-dimercaptosuccinate (Mi-ADMS), a new dimercaptosuccinic acid (DMSA) analog with enhanced lipophilic properties, was evaluated for potential developmental toxicity. Intraperitoneal injections of Mi-ADMS were given to female Swiss mice (0, 47.5, 95, and 190 mg/kg) on gestational d 6-15. The maternal clinical status was monitored daily during treatment. At termination (gestational d 18), dams were evaluated for clinical status and gestational outcome. Each live fetus was weighed and examined for external, visceral, and skeletal abnormalities. Although no maternal mortality was observed, treatment with 95 and 190 mg/kg resulted in maternal toxicity, manifested as reduced body weight gain during treatment and increased relative liver weight. Embryo/fetal toxicity, consisting of a significant increase in the number of late resorptions as well as in the percentage of postimplantation loss, reduced (nonsignificant) fetal body weight, and an increase in the incidence of skeletal defects, was also observed at 190 mg/kg/d. However, no treatment-related external or soft-tissue malformations or developmental variations were found in any group. The no-observed-adverse-effect level (NOAEL) for maternal toxicity was 47.5 mg/kg/d, whereas the NOAEL for developmental toxicity was 95 mg/kg/d. These results indicate that Mi-ADMS did not produce developmental toxicity in mice in the absence of maternal toxicity.

Abnormalities, Drug-Induced↗

Developmental toxicity of acephate by gavage in mice.

Acephate (O,S - dimethyl acetyl phosphoramidothioate), an organophosphate insecticide, was evaluated for its potential to produce developmental toxicity in mice after oral administration. Pregnant ICR (CD-1) mice were given sublethal doses of 0 (distilled water), 7, 14, and 28 mg/kg/day acephate by gavage on Gestation Days 6 through 15. Maternal effects in the 28 mg/kg/day dose group included cholinergic signs, decreased body weight at 15 and 18 days of gestation, and decreased absolute and relative brain weight. Placental weight was also decreased and liver weight was increased in the high dose group. Absolute and relative brain weight was decreased in the 14 mg/kg/day group. No maternal effects were apparent in the 7 mg/kg/day dose group. Maternal exposure to acephate during organogenesis significantly affected the number of implantations, number of live fetuses, number of early resorptions, mean fetal weight, and the incidence of external and skeletal malformations in the 28 mg/kg/day dose group. No visceral malformations were observed. On the basis of the present results acephate showed maternal and developmental toxicity at 28 mg/kg/day.

Abnormalities, Drug-Induced↗

Developmental toxicity evaluation of sodium thioglycolate administered topically to Sprague-Dawley (CD) rats and New Zealand White rabbits.

BACKGROUND: Sodium thioglycolate, which has widespread occupational and consumer exposure to women from cosmetics and hair-care products, was evaluated for developmental toxicity by topical exposure during the embryonic and fetal periods of pregnancy METHODS: Timed-mated Sprague-Dawley rats (25/group) and New Zealand White (NZW) rabbits (24/group) were exposed to sodium thioglycolate in vehicle (95% ethanol:distilled water, 1:1) by unoccluded topical application on gestational days (GD) 6-19 (rats) or 6-29 (rabbits) for 6 hr/day, at 0, 50, 100, or 200 mg/kg body weight/day (rats) and 0, 10, 15, 25, or 65 mg/kg/day (rabbits). At termination (GD 20 rats; GD 30 rabbits), fetuses were examined for external, visceral, and skeletal malformations and variations. RESULTS: In rats, maternal topical exposure to sodium thioglycolate, at 200 mg/kg/day (the highest dose tested) on GD 6-19, resulted in maternal toxicity, including reduced body weights and weight gain, increased relative water consumption and one death. Treatment-related increases in feed consumption and changes at the applicationsite occurred at all doses, in the absence of increased body weights or body weight change. Fetal body weights/litter were decreased at 200 mg/kg/day, with no other embryo/fetal toxicity and no treatment-related teratogenicity in any group. In rabbits, maternal topical exposure to sodium thioglycolate on GD 6-29 resulted in maternal dose-related toxicity at the dosing site in all groups; no maternal systemic toxicity, embryo/fetal toxicity, or treatment-related teratogenicity were observed in any group. CONCLUSIONS: A no observed adverse effect level (NOAEL) was not identified for maternal toxicity in either species with the dosages tested. The developmental toxicity NOAEL was 100 mg/kg/day (rats) and > or = 65 mg/kg/day (rabbits; the highest dose tested). The clinical relevance of theses study results is uncertain because no data were available for levels, frequency, or duration of exposures in female workers or end users.

Abnormalities, Drug-Induced↗

The reproductive and developmental toxicity of indium in the Swiss mouse.

Indium is increasingly used in a variety of industries, and while there are few studies of its developmental toxicity, ther are no reports of its potential reproductive toxicity. These studies were undertaken to investigate the possible reproductive toxicity of indium and to determine the relative vulnerability of males and females. We used, initially, a 21-day combined developmental/reproductive toxicity protocol. Oral exposures to InCl3 ( < or = 250 mg/kg) were without effect on the male reproductive system or liver. A kidney effect was demonstrated in males by a decrease in urinary N-acetyl glucosaminidase. The ability of females to become pregnant was unaffected. However, fetal development was adversely affected, manifested as increased intrauterine deaths in the presence of reduced maternal weight gain. A developmental toxicity study identified no increase in fetal malformations, but verified the increased fetal deaths, in the absence of effects on adjusted maternal body weight. In vitro toxicity studies showed that the embryolethality was at least in part a result of direct toxicity to the conceptus, with effective doses in the low micromolar range. A limited disposition study showed that fetuses contained low micromolar concentrations of indium, more indium than maternal liver, and comparable to levels that were toxic in vitro. Although studies of greater exposure duration are required for risk assessment, these data indicate that fetal development is likely to be more affected by indium than female or male reproduction, with adverse effects occurring at low micromolar levels in vivo and at exposures that may or may not affect body weight.

Abnormalities, Drug-Induced↗

Behavioral evaluations in developmental toxicity testing: MARTA survey results.

During 1991, the Middle Atlantic Reproduction and Teratology Association (MARTA) conducted a survey of laboratories performing behavioral evaluations as part of GLP developmental toxicity studies. This survey was conducted to determine the extent to which an "industry standard" had evolved for behavioral test batteries. The most commonly used developmental parameters were eye opening, pinna unfolding, and sexual maturation (physical landmarks); surface righting, pupil constriction, and nonautomated acoustic startle (reflexive landmarks). Locomotor activity was used by 80% of the laboratories. The majority (76%) of laboratories conducted at least one learning and/or retention evaluation; nearly one-fourth of the laboratories routinely performed two. The most common learning tests were watermaze (primarily a simple two-choice discrimination task) and passive avoidance. Automated startle paradigms (habituation, prepulse modification, and/or startle elicitation) were evaluated by 28% of the laboratories. This survey showed a remarkable similarity in methodology across laboratories and a progressive increase in the number of GLP studies that included behavioral assessments. The results indicate that behavioral tests have become a common component of developmental toxicity assessments of pharmaceuticals.

Animals↗

Developmental toxicity evaluation of phthalic acid, one of the metabolites of phthalic acid esters, in rats.

The objective of this study was to evaluate the developmental toxicity of phthalic acid (PA), which is one of the metabolites of phthalic acid esters (PAEs). Pregnant rats were given PA at a dose of 0 (control), 1.25, 2.5, or 5.0% in the diet on day 7 through day 16 of pregnancy. Average daily intakes of PA were 1021 mg/kg for the 1.25% group, 1763 mg/kg for the 2.5% group, and 2981 mg/kg for the 5.0% group. Maternal toxicity occurred in the 2.5 and 5.0% groups as can be seen by significant decreases in the maternal body weight gain and food consumption during the administration period. No significant changes in maternal parameters were found in the 1.25% group. Neither deaths nor clinical signs of toxicity were noted in any groups. No significant changes induced by PA were detected in the incidence of postimplantation loss and number and sex ratio of live fetuses. Significant decreases in the weight of male fetuses and number of ossification center of the caudal vertebrae were found in the 5.0% group. Morphological examinations of fetuses revealed no evidence of teratogenesis. Thus it appears unlikely that PA may be responsible for the production of the developmental toxicity of PAEs.

Animals↗

Ground and surface water developmental toxicity at a municipal landfill: description and weather-related variation.

Contaminated groundwater poses a significant health hazard and may also impact wildlife such as amphibians when it surfaces. Using FETAX (Frog Embryo Teratogenesis Assay-Xenopus), the developmental toxicity of ground and surface water samples near a closed municipal landfill at Norman, OK, were evaluated. The groundwater samples were taken from a network of wells in a shallow, unconfined aquifer downgradient from the landfill. Surface water samples were obtained from a pond and small stream adjacent to the landfill. Surface water samples from a reference site in similar habitat were also analyzed. Groundwater samples were highly toxic in the area near the landfill, indicating a plume of toxicants. Surface water samples from the landfill site demonstrated elevated developmental toxicity. This toxicity was temporally variable and was significantly correlated with weather conditions during the 3 days prior to sampling. Mortality was negatively correlated with cumulative rain and relative humidity. Mortality was positively correlated with solar radiation and net radiation. No significant correlations were observed between mortality and weather parameters for days 4-7 preceding sampling.

Animals↗

Developmental toxicity evaluation of 1,2,3,4-butanetetracarboxylic acid in Sprague Dawley (CD) rats.

1,2,3,4-butanetetracarboxylic acid (BTCA), proposed as a formaldehyde substitute in the treatment of permanent press fabrics, was evaluated for developmental toxicity. Timed-mated CD rats (25 per group) received BTCA 250, 500, or 1000 mg/kg/day or vehicle (deionized/distilled water) by gavage on gestational days (gd) 6 through 19. Maternal feed and water consumption, body weight, and clinical signs were monitored throughout gestation. At termination (gd 20), confirmed-pregnant females (21 to 25 per group) were evaluated for clinical status and gestational outcome; live fetuses were examined for external, visceral, and skeletal malformations. One maternal death, reduced body weight, and reduced weight gain were noted at the high dose; confirmed pregnancy rates were 84 to 100% for each group. There were no treatment-related effects on fetal growth, survival, or morphologic development. The maternal toxicity NOAEL and LOAEL are 500 and 1000 mg/kg/day, respectively. The developmental toxicity NOAEL is > or = 1000 mg/kg/day, and the LOAEL was not established in this study.

Administration, Oral↗