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B A Schwetz

Publications and source records attributed to B A Schwetz.

At least 19 recordsLinked to original sources

Criteria for judging the relative toxicity of chemicals from developmental toxicity data: a workshop summary.

In summary, participants of this workshop confirmed that many criteria need to be considered when interpreting the results of developmental toxicity studies. All aspects of developmental toxicity are of interest, but their importance to the consideration varies along the continuum from hazard detection to risk estimation. As with many other manifestations of toxicity, potential developmental risk to humans is a function of exposure and developmental toxicity, the latter reflecting the inherent potential of a substance to cause an adverse effect under some defined condition. All of the criteria discussed in this workshop were considered to be of some importance in characterizing the developmental toxicity of a substance, their relative importance being a function of the question under consideration. Proper interpretation of developmental toxicity data, which must include prenatal as well as postnatal observations to be considered complete, should take into account the differential toxicity to the mother and the conceptus, the nature of the developmental toxicity observed, and the consistency of response between species. The proximity of human exposure levels to dose levels that are developmentally toxic in animals is a major determinant of the potential for hazard to humans. Mechanistic and pharmacokinetic knowledge can modulate interpretation of descriptive data and refine the prediction of human hazard. Recognizing that in vitro studies will never completely recapitulate the results of in vivo studies, the committee to update the "Smith list" will move forward taking the discussions of this workshop into account.

Animals

The developmental toxicity of ethylene glycol diethyl ether in mice and rabbits.

Timed-pregnant CD-1 outbred Albino Swiss mice and New Zealand White rabbits were dosed by gavage with ethylene glycol diethyl ether (EGdiEE) in distilled water during major organogenesis. Mice were dosed on Gestational Days (gd) 6 through 15 (0, 50, 150, 500, or 1000 mg/kg/day) and rabbits on gd 6 through 19 (0, 25, 50, or 100 mg/kg/day). Maternal clinical status was monitored daily during treatment. At termination (gd 17, mice; gd 30, rabbits), confirmed-pregnant females (22-24 per group, mice; 26-32 per group, rabbits) were evaluated for clinical status and gestational outcome; each live fetus was examined for external, visceral, and skeletal malformations. In mice, no maternal mortality was observed, but maternal body weight gain during gestation and treatment, and at termination was reduced at 1000 mg/kg/day. The reduction of maternal body weight gain during gestation was secondary to embryo/fetal toxicity, i.e., reduced gravid uterine weight as a consequence of decreased litter size and fetal weight. The no-observed adverse effect level (NOAEL) for developmental toxicity was 50 mg/kg/day. At greater than or equal to 150 mg/kg/day the number of litters of mice with malformed fetuses was increased. At greater than or equal to 500 mg/kg/day fetal body weight was reduced, and malformation incidence was significantly increased. Exencephaly and fused ribs were observed most often. In rabbits, maternal body weight was unaffected by treatment even though 6% maternal mortality was observed at 100 mg/kg/day. The developmental NOAEL was 25 mg/kg/day. Malformations were increased at greater than or equal to 50 mg/kg/day; short tail, small spleen, fused sternebrae, and fused rib cartilage were observed most often. In summary, oral administration of EGdiEE to mice and rabbits during organogenesis produced profound adverse developmental effects even in the absence of significant maternal toxicity. Developmental effects in rabbits were more varied.

Abnormalities, Drug-Induced

Evaluation of the potential for developmental toxicity in rats and mice following inhalation exposure to tetrahydrofuran.

Sprague-Dawley rats and Swiss (CD-1) mice were exposed to 0, 600, 1800, or 5000 ppm THF (a four-carbon cyclic ether, widely used as an industrial solvent) vapors, 6 hr/day, 7 days/week (6-19 days of gestation (DG) for rats; 6-17 DG for mice). Body weights of pregnant rats in the 5000 ppm group were reduced at euthanization. There were no effects on the percentage of live rat fetuses/litter or on the fetal sex ratio. Fetal body weight was significantly reduced for the 5000 ppm group, but the incidence of abnormalities was not increased. Mice in the 1800 and 5000 ppm groups were sedated during exposure; approximately 27% of the mice in the 5000 ppm group died. Mean body and uterine weights of mice were reduced for the 1800 and 5000 ppm groups at euthanization (18 DG), but adjusted maternal weight gain was not affected at 1800 ppm. There was a reduction in the percentage of live fetuses/litter for the mice in 1800 and 5000 ppm groups (95% resorptions in the 5000 ppm group). Fetal weight and sex ratio in mice were not affected. An increase in the incidence of reduced sternebral ossifications was correlated to THF concentration, although differences between groups were not statistically significant. There were no increases in the incidences of other malformations or variations. These results suggest that THF may be embryotoxic in mice, but if the conceptus survives, development as assessed by this experimental design continues in a normal fashion. The no-observable-adverse-effect level (NOAEL) for maternal toxicity was 1800 ppm in both rats and mice. The NOAEL for developmental toxicity was 1800 ppm in rats and 600 ppm in mice.

Abnormalities, Drug-Induced

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.

Abnormalities, Drug-Induced

The developmental toxicity of diethylene and triethylene glycol dimethyl ethers in rabbits.

Diethylene glycol dimethyl ether (diEGdiME) and triethylene glycol dimethyl ether (triEGdiME), widely used organic solvents, are structurally related to several compounds that produce reproductive and developmental toxicity, including teratogenicity in laboratory animals. In the present studies, diEGdiME (0, 25, 50, 100, or 175 mg/kg/day) or triEGdiME (0, 75, 125, 175, or 250 mg/kg/day) were administered by gavage in distilled water to timed-pregnant New Zealand white rabbits (15-25 dams/group) during major organogenesis [Gestational Days (gd) 6-19]. Treated females were euthanized on gd 30, uterine contents were examined, and live fetuses were examined for morphological alterations. In the diEGdiMe study, evidence of maternal toxicity, per se, was observed only at 175 mg/kg/day with 15% mortality among treated females compared to 4% among controls. No significant maternal toxicity was observed in the 25 mg/kg/day group, and only minimal maternal toxicity (decreased maternal weight gain during treatment) was observed at 50 and 100 mg/kg/day compared to the vehicle control group. The no-observed-adverse-effect level for developmental toxicity in rabbits for diEGdiME was 50 mg/kg/day. The incidences of prenatal mortality and malformed live fetuses were significantly above controls at 100 and 175 mg/kg/day. Malformations observed most frequently included fusion of ribs to each other and hydronephrosis; clubbing of the limbs without underlying bone deformities, a variation, was also observed. In the triEGdiME study, clinical signs of toxicity were minimal and there was no increased maternal mortality. Maternal body weight and gravid uterine weight were significantly reduced at 250 mg/kg/day, whereas maternal weight gain during treatment was significantly depressed at doses of 175 mg/kg/day and above.(ABSTRACT TRUNCATED AT 250 WORDS)

Animals

Developmental toxicity of inhaled methyl ethyl ketone in Swiss mice.

Methyl ethyl ketone (MEK) is a widely used industrial solvent to which there is considerable human exposure. To assess the potential for MEK to cause developmental toxicity in rodents, groups of Swiss (CD-1) mice were exposed to 0, 400, 1000, or 3000 ppm MEK vapors 7 hr/day on Days 6-15 of gestation. Groups consisted of about 30 bred females each. Exposure of pregnant mice to these concentrations of MEK did not result in overt maternal toxicity although there was a slight, treatment-related increase in relative liver weight which was statistically significant in the 3000 ppm group. Mild developmental toxicity was observed in the 3000 ppm group in the form of a reduction in mean fetal body weight. This reduction was statistically significant for the males only, although the relative decrease from the control values was the same for both sexes. There was no increase in the incidence of resorptions or the number of litters with resorptions among mice exposed to MEK. There was no significant increase in the incidence of any single malformation, but several malformations which were not observed in the concurrent control group or the controls of contemporary studies were present at a low incidence--cleft palate, fused ribs, missing vertebrae, and syndactyly. There was also a significant trend for increased incidence of misaligned sternebrae, a developmental variation. In summary, pregnant Swiss (CD-1) mice were relatively insensitive to the toxic effects of MEK at the inhaled concentrations used in this study. However, the offspring of the mice exhibited significant signs of developmental toxicity at the 3000 ppm exposure level.(ABSTRACT TRUNCATED AT 250 WORDS)

Abnormalities, Drug-Induced

In vitro teratology.

The purpose of this conference was to reevaluate the need for and use of in vitro teratology assays; to examine the validation process for in vitro tests; and to discuss progress in the validation of in vitro teratology screens. Participants enthusiastically supported further development of short-term in vivo and in vitro systems both as prescreens for developmental toxicity and as experimental systems to explore mechanisms of action of toxicants. The group strongly endorsed the development of an updated reference list ("gold standard") of known developmental toxicants and nontoxicants as essential to further progress in developing and validating prescreening efforts. Independently, an expert group should further evaluate the performance characteristics for a validated prescreen. The limits of usefulness of prescreens for product development, regulatory use, and mechanistic investigations need to be clearly defined. Finally, too few in vitro teratology prescreens have been evaluated under multiple-laboratory conditions with common, agreed-upon test agents to draw firm conclusions regarding the merit and reproducibility of in vitro teratology prescreens. There was general agreement regarding the need to move several of the assays further along the validation pathway, at least using a short list of reference compounds.

Animals

Excretion of high concentrations of cimetidine and ranitidine into rat milk and their effects on milk composition and mammary gland nucleic acid content.

The excretion of cimetidine and ranitidine into rat milk following single or multiple oral doses and the subsequent effects on their suckling pups and on milk composition and milk synthesis were investigated. Following a single dose of [3H]cimetidine, peak milk cimetidine concentrations were maintained from 1 until 4 hr, while plasma concentrations peaked at 10% of the milk level at 30 min and then declined. Multiple doses of cimetidine (18 or 180 mg/kg/day) on Days 13-16 of lactation led to milk cimetidine concentrations of 17 and 113 micrograms/ml. The milk/plasma ratios far exceeded the theoretical milk/plasma ratio of 2.0. Ranitidine concentrations in rat milk following ranitidine treatment (4.5 or 45 mg/kg/day) were also greater (6.8-15 times) than in plasma, but only slightly greater than the predicted ratio of 5.0. There were no changes in liver weight or in hepatic aminopyrine N-demethylase activity in the cimetidine- or ranitidine-treated dams or their pups. Cimetidine treatment had no effect on milk lipid, solid, or protein content, but at 180 mg/kg/day, caused a significant increase in milk lactose. The RNA/DNA ratio in the mammary gland was significantly increased by cimetidine, suggesting increased milk synthesis. Ranitidine had no effect on milk composition or on mammary gland RNA, DNA, or RNA/DNA. Therefore, high concentrations of cimetidine and ranitidine were excreted into rat milk, but no deleterious effects on the suckling pups, or the composition of the milk, or on the milk synthetic activity were observed.

Aminopyrine N-Demethylase

Arsine: absence of developmental toxicity in rats and mice.

Arsine gas is a potent hemolytic agent but the effects of exposure to tolerated concentrations on pregnancy and prenatal development have not been reported. In the present evaluation, groups of bred mice and rats were exposed to arsine at concentrations of 0.025, 0.5, or 2.5 ppm on Gestation Days (gd) 6 through 15. Animals were killed on gd 17 (mice) or on gd 20 (rats) and endpoints of maternal and developmental toxicity were evaluated. In rats, maternal spleens were enlarged in the 2.5 ppm group and there was a decrease in packed red cell volume in pregnant rats. Fetuses weighed more than in the control group but other endpoints of developmental toxicity were not affected by arsine exposure. In another experiment involving separate groups of rats, the arsenic content of maternal blood and fetal livers increased with increasing atmospheric arsine concentrations, as assessed on gd 20. In mice, maternal spleen size was significantly increased in the 2.5 ppm group. The number of live fetuses, mean fetal body weight, and percentages of resorptions or malformations per litter were not affected by arsine exposure. In conclusion, arsine at atmospheric concentrations that caused increases in maternal spleen size and measurable levels of arsenic in maternal blood and fetal livers did not adversely affect endpoints of developmental toxicity.

Air Pollutants, Occupational

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.

Acrylamide

Overview of reproductive and developmental toxicity studies of 1,3-butadiene in rodents.

A series of studies to further evaluate the developmental and reproductive toxicity of inhaled 1,3-butadiene was sponsored by the National Toxicology Program. Pregnant Sprague-Dawley rats (24-28/group) and Swiss (CD-1) mice (18-22/group) were exposed to atmospheric concentrations of 0, 40, 200, or 1000 ppm 1,3-butadiene for 6 hr/day on days 6 through 15 of gestation (dg) and killed on dg 18 (mice) or dg 20 (rats). Subsequently, the uterine contents were evaluated; individual fetal body weights were recorded; and external, visceral, and skeletal examinations were performed. In rats, maternal toxicity was observed in the 1000-ppm group in the form of reduced extragestational weight gain and, during the first week of treatment, decreased body weight gain. Under these conditions, there was no evidence of developmental toxicity in rats. In contrast, results of the mouse developmental toxicity study indicated that the fetus may be more susceptible than the dam to inhaled 1,3-butadiene. Maternal toxicity was observed in mice at the 200- and 1000-ppm 1,3-butadiene exposure levels, whereas 40 ppm and higher concentrations of 1,3-butadiene caused significant exposure-related reductions in the mean body weights of male fetuses. Mean body weights of female fetuses were also reduced at the 200- and 1000-ppm exposure levels. No increased incidence of malformations was observed in either study. Other studies addressing male reproductive and mutagenesis end points were performed with B6C3F1 mice (sperm-head morphology) and Swiss (CD-1) mice (dominant lethal study).(ABSTRACT TRUNCATED AT 250 WORDS)

Administration, Inhalation

The developmental toxicity of orally administered theophylline in rats and mice.

Theophylline (THEO), a widely prescribed anti-asthmatic, was evaluated for developmental toxicity. It was administered continuously on Gestational Days 6 through 15 to pregnant Sprague-Dawley (CD) rats in the feed (0, 0.15, 0.30, or 0.40%) and to pregnant Swiss (CD-1) mice in the drinking water (0, 0.075, 0.15, or 0.20%). Estimated intake of THEO for rats was 0, 124, 218, or 259 mg/kg/day, while for mice it was 0, 282, 372, or 396 mg/kg/day. In rats, maternal weight gain parameters (weight gain during gestation and treatment, as well as corrected weight gain) decreased at 0.40%. While food consumption was lower only in the 0.40% treatment group, water consumption was higher in all treated groups. There was a dose-related decreasing trend in gravid uterine weight. The number of live fetuses per litter decreased at 0.40% and the average male and female fetal weight per litter decreased at 0.30 and 0.40%. There was no increase in malformations. In mice, maternal corrected body weight and weight gain during gestation decreased at 0.15 and 0.20%, and weight gain during treatment and gravid uterine weight decreased at 0.20%. Water consumption was reduced by as much as 30-45% of controls at 0.15 and 0.20%, respectively, while food consumption did not change with THEO treatment. There was an increase in percentage resorptions per litter and a decrease in the average male and female fetal weight per litter at 0.15 and 0.20%. An increasing trend was noted for percentage malformed fetuses per litter, and percentage litters with externally malformed fetuses were slightly increased in the mid- and high-dose groups. However, these increases were not statistically significant. In summary, there were developmental effects seen in rats at a dose (0.30%) that did not produce overt maternal toxicity, but the adverse developmental effects in mice were observed at doses that caused reduced maternal water consumption and body weight gain. It is possible that water deprivation contributed to the effects seen in mice after THEO treatment. For maternal toxicity, no observable adverse effect levels (NOAELs) were 218 mg/kg for rats and 282 mg/kg for mice. NOAELs for developmental toxicity were 124 mg/kg for rats and 282 mg/kg for mice. These NOAELs are approximately 10- to 30-fold greater than doses required to maintain humans on serum THEO concentrations that are clinically useful.

Abnormalities, Drug-Induced

Approaches used by the US National Toxicology Program in assessing the toxicity of chemical mixtures.

The US National Toxicology Program has made a definite commitment towards improving the understanding and predictability of the toxicity of chemical mixtures. The commitment has consisted of a thorough review by the National Research Council of the state of the art of complex mixture testing and strategy for in vivo tests as well as a series of laboratory studies to better characterize the toxicity of selected chemical mixtures and research programmes to improve our ability to predict the toxicological properties of other mixtures.

Animals

Determination of diphenhydramine in rat milk and plasma and its effects on milk composition and mammary gland nucleic acids.

To study the excretion of diphenhydramine into rat milk, milk and plasma concentrations of diphenhydramine were determined in lactating rats after single or multiple oral doses. Four hours after a single dose of 40 or 100 mg/kg of diphenhydramine, milk concentrations of the drug averaged 0.30 and 2.2 micrograms/mL, respectively, in two experiments, and the milk:plasma ratios ranged from 4.4 to 7.5. Multiple doses did not significantly affect the plasma or milk concentrations or the milk:plasma ratios, which were similar to the theoretical milk:plasma ratio based on pH partitioning for this compound (i.e., 4.0). Although the concentration of diphenhydramine was higher in milk than in plasma, the estimated dose received by the pups (0.057 mg/kg/d) based on the milk concentrations was much lower than that given to the mother. Oral diphenhydramine treatment at doses which significantly reduced maternal food consumption had no effect on milk solid, lipid, protein, or lactose concentrations, nor on mammary gland RNA or DNA content, indicating that diphenhydramine did not adversely affect lactation.

Animals

Developmental toxicity screen: results of rat studies with diethylhexyl phthalate and ethylene glycol monomethyl ether.

The purpose of these investigations was to develop a protocol for an in vivo developmental toxicity screen (DETS) that would provide sufficient data to determine whether to 1) do a full developmental toxicity evaluation without additional range-finding studies, or, depending on the results, to 2) do no further testing of a chemical. In order to evaluate this screen, we compared results obtained by using the DETS protocol with results of previously conducted developmental toxicity evaluations of diethylhexyl phthalate (DEHP) and ethylene glycol monomethylether (EGME). Five groups (n greater than or equal to 17) of F344 rats were treated on days 6-15 of gestation by dosed feed (DEHP levels = 0, 0.5, 1.0, 1.5, 2.0%) or gavage (EGME doses = 0, 12.5, 25, 50, 100 mg/kg/day). One half of the rats in these studies were killed on day 16 of gestation, and the remaining animals were allowed to deliver litters which were killed on day 4. EGME caused only a small decrease in maternal weight gain during treatment (100 mg/kg group) that was accompanied by a decrease in gravid uterine weight. The percentage of resorptions was increased in the 50 and 100 mg/kg groups. The number of live pups was decreased in the 25, 50, and 100 mg/kg groups, and litter weight and postnatal survival were decreased in the 100 mg/kg group. These results are consistent with those reported in developmental toxicity studies on EGME conducted by the inhalation and dermal routes. With DEHP, there were treatment-related reductions in maternal body weight and weight gain. There was also a nonstatistical increase in percentage of resorptions per litter that was also observed, but at relatively high levels, in a definitive study in which F344 dams were treated on days 0-20 of gestation. The results of studies on these two chemicals compare well with published results and would have led to the selection of proper dose levels for subsequent FDA segment 2 studies.

Animals

Establishing aerosol exposure concentrations for inhalation toxicity studies.

Criteria for the selection of aerosol concentrations to be used in inhalation studies assessing the toxicity and carcinogenicity of chemical substances were discussed by the authors in a meeting sponsored by the National Toxicology Program. Concepts in the design of aerosol inhalation studies emerged from that meeting and are being communicated through this publication. Inhalation studies assessing the toxicity and carcinogenicity of aerosols have often used maximum exposure levels on the basis of technological feasibility. Evidence has now accumulated that the amount of pulmonary burden of deposited particles impacts on particle clearance above some as yet not well-defined exposure concentration. The sequelae are such that lung clearance decreases with increased particulate burden to the point of approaching complete cessation. This paper focuses on the major determinants in establishing maximal aerosol concentrations for use in inhalation toxicity studies with special emphasis on experimental design features to assess lung retention. The subject matter of this paper is a rapidly developing area in terms of knowledge. Accordingly, the contents of this article are intended as guidelines and not as absolute rules for the conduct and interpretation of inhalation exposure studies.

Administration, Inhalation

Toxicology studies of a chemical mixture of 25 groundwater contaminants. III. Male reproduction study in B6C3F1 mice.

A mixture of chemicals has been developed that models contaminated groundwater around hazardous waste sites. We investigated the effects of this mixture on spermatogenesis in B6C3F1 mice. The animals consumed three different concentrations of this mixture for 90 days, after which time they were euthanatized. Although there was a concentration-related decrease in the amount of fluid consumed at the higher two concentrations, there were no differences in body weight among the groups. Similarly, there was no effect of mixture consumption upon the histology of liver, kidney, testis, epididymis, or seminal vesicles or upon the absolute organ weights of these organs. Kidney weight relative to body weight was increased in the high dose group. Epididymal sperm number and testicular spermatid count were not affected by treatment. These studies show that, at exposure levels that decrease fluid intake and increase adjusted kidney weight, there were no effects of this mixture on gametogenesis in male mice.

Animals

Developmental toxicity of 1,1,1-trichloroethane in CD rats.

1,1,1-Trichloroethane (TCEN), a major industrial and household solvent, was evaluated for pre- and postnatal developmental effects in Sprague-Dawley rats. This study was designed to assess the repeatability of a report (S.C. Dapson, D.E. Hutcheon, and D. Lehr, Teratology 29, 25A, 1984) that indicated that 10 ppm TCEN in drinking water caused cardiac malformations in developing rats. In the present study, TCEN (97% pure) was administered in the drinking water at target concentrations of 3, 10, and 30 ppm, using 0.05% Tween 80 as an emulsifying agent. Two control groups, one receiving deionized/filtered water and the other receiving a vehicle control solution containing 0.05% Tween 80 and 0.9 ppm 1,4-dioxane, a stabilizing agent found in the bulk chemical, were also included. Male and female breeders (more than 30 per group) were exposed to the control solutions or test compound for 14 consecutive days prior to cohabitation and for up to 13 days during the cohabitation phase. Sperm-positive females (24-29 per group) continued to be exposed to these formulations during pregnancy and lactation to Postnatal Day (PND) 21. Parental animals exhibited a slight aversion to the 30-ppm drinking water during the premating exposure. No significant effect on reproductive competence of the parental animals or postnatal growth and development of the offspring to PND 21 was noted. A slight increase in mortality from implantation to PND 1, possibly due to high mortality in one litter, was observed in the 30-ppm dose group. There was no indication of an increase in the incidence of cardiac or other malformations in PND 21 pups. In summary, TCEN administered at 3, 10, and 30 ppm in the drinking water had no significant effect on the morphological development of CD rats.

Animals