Evaluation of the potential developmental toxicity of cyclododecatriene (CDDT)

The potential maternal and developmental toxicity of cyclododecatriene (CDDT) was assessed in rats. Groups of 22 time-mated female Crl:CD (SD) BR rats were exposed by inhalation (whole-body, 6 h/day) to either 0 (control), 10, 25, or 67 ppm CDDT over days 6-20 of gestation (days 6-20 G); the day of copulation plug detection was designated day 0 G. The dams were euthanized on day 21 G, and their abdominal and thoracic viscera were examined grossly. The fetuses were weighed, sexed, and examined for external, visceral, and skeletal alterations. Evidence of maternal toxicity was seen at 25 and 67 ppm. There were compound-related reductions in maternal body weight and food consumption parameters as well as increased occurrences of wet and stained fur at these exposure levels. Developmental toxicity evident as reduced mean fetal weight and delayed skeletal ossification was seen only at 67 ppm. There was no evidence of either maternal or developmental toxicity at 10 ppm. Thus, the no-observed-effect level (NOEL) for maternal toxicity was 10 ppm, and the NOEL for developmental toxicity was 25 ppm. Because developmental toxicity was observed only after exposures that also produced signs of maternal toxicity, CDDT was not considered to be a selective developmental toxicant in the rat.     

Evaluation of the Potential Developmental Toxicity of Cyclododecatriene (CDDT)

Abstract

The potential maternal and developmental toxicity of cyclododecatriene (CDDT) was assessed in rats. Groups of 22 time-mated female Crl:CD® (SD) BR rats were exposed by inhalation (whole-body, 6 h/day) to either 0 (control), 10, 25, or 67 ppm CDDT over days 6–20 of gestation (days 6–20 G); the day of copulation plug detection was designated day 0 G. The dams were euthanized on day 21 G, and their abdominal and thoracic viscera were examined grossly. The fetuses were weighed, sexed, and examined for external, visceral, and skeletal alterations. Evidence of maternal toxicity was seen at 25 and 67 ppm. There were compound-related reductions in maternal body weight and food consumption parameters as well as increased occurrences of wet and stained fur at these exposure levels. Developmental toxicity evident as reduced mean fetal weight and delayed skeletal ossification was seen only at 67 ppm. There was no evidence of either maternal or developmental toxicity at 10 ppm. Thus, the no-observed-effect level (NOEL) for maternal toxicity was 10 ppm, and the NOEL for developmental toxicity was 25 ppm. Because developmental toxicity was observed only after exposures that also produced signs of maternal toxicity, CDDT was not considered to be a selective developmental toxicant in the rat.     

Inhalation developmental toxicity and reproduction studies with cyclohexane

The reproductive and developmental toxicity of cyclohexane was assessed in a two-generation reproduction study with Crl:CD BR rats and in developmental toxicity studies with Crl:CD BR rats and Hra:(NZW)SPF rabbits. The animals were exposed whole-body to atmospheric concentrations of 0, 500, 2000, or 7000 ppm cyclohexane. In the two-generation reproduction study, parental effects included statistically significantly lower mean body weight, overall mean body weight gain, and overall mean food efficiency for P1 and F1 females of the 7000 ppm level and statistically significantly lower mean body weight for F1 males of that level. Adult rats exposed to 2000 ppm cyclohexane and above exhibited a transient diminished or absent response to a sound stimulus while in the chambers during exposure. Mean pup weight was statistically significantly lower than control from lactation day 7 throughout the remainder of the 25-day lactation period for both F1 and F2 7000 ppm litters. Changes observed at 500 ppm were either considered not to be compound related or not adverse. Therefore, the systemic-toxicity no-observed-effect level (NOEL) was 500 ppm and the reproductive NOEL was 2000 ppm. The reproductive NOEL was based solely on the decreased pup weights in both the F1 and F2 generations observed at 7000 ppm. In the developmental toxicity studies, only the rats showed evidence of maternal toxicity. For rats in the 7000 ppm group, statistically significant reductions were observed in overall maternal body weight gain and overall maternal food consumption for the treatment period. Rats exposed to 2000 ppm cyclohexane and above again exhibited a transient diminished or absent response to a sound stimulus while in the chambers during exposure. Therefore, for rats, the maternal no-observed-effect level (NOEL) was 500 ppm. In the rabbit developmental toxicity study, no compound-related maternal effects were observed at concentration levels of 7000 ppm and below. Therefore, the maternal NOEL for rabbits was 7000 ppm. No compound-related evidence of developmental toxicity was observed at any test concentration in either species. Therefore, the developmental NOEL for both species was 7000 ppm, the highest concentration tested.     

EVALUATION OF THE POTENTIAL DEVELOPMENTAL TOXICITY OF 3-AMINOPENTANENITRILE (3-APN) IN THE RAT

The potential developmental toxicity of 3-aminopentanenitrile (3-APN) was assessed in rats. Groups of 25 time-mated female Crl:CD®(SD)IGS BR rats were orally gavaged at daily dose levels of 0, 5, 30, 100 or 300 mg/kg over days 6–20 of gestation (days 6–20G); the day of copulation plug detection was designated day 0G. The dams were euthanized on day 21G and their abdominal and thoracic viscera were examined grossly. The fetuses were weighed, sexed, and examined for external, visceral, and skeletal alterations. Evidence of maternal and developmental toxicity was seen at 100 and 300 mg/kg. Regarding maternal toxicity, there were compound-related, statistically significant reductions in maternal body weight and food consumption at 100 and 300 mg/kg. The incidence of alopecia was significantly increased at these levels as well. Regarding developmental toxicity, mean fetal weight was slightly but significantly reduced at 100 and 300 mg/kg. In addition, at 300 mg/kg, there were significant increases in several skeletal variations (wavy ribs and skull, rib, and vertebral ossification delays) consistent with developmental delay. There was no evidence of either maternal or developmental toxicity at 5 or 30 mg/kg. Thus, the maternal and developmental no-observed-effect level (NOEL) was 30 mg/kg. Because developmental toxicity was observed only after administration of doses that also produced signs of maternal toxicity, 3-APN is not considered to be a selective developmental toxicant in the rat.     

Evaluation of the potential developmental toxicity of 3-aminopentanenitrile (3-APN) in the rat

The potential developmental toxicity of 3-aminopentanenitrile (3-APN) was assessed in rats. Groups of 25 time-mated female Crl:CD(SD)IGS BR rats were orally gavaged at daily dose levels of 0, 5, 30, 100 or 300 mg/kg over days 6-20 of gestation (days 6-20G); the day of copulation plug detection was designated day 0G. The dams were euthanized on day 21G and their abdominal and thoracic viscera were examined grossly. The fetuses were weighed, sexed, and examined for external, visceral, and skeletal alterations. Evidence of maternal and developmental toxicity was seen at 100 and 300 mg/kg. Regarding maternal toxicity, there were compound-related, statistically significant reductions in maternal body weight and food consumption at 100 and 300 mg/kg. The incidence of alopecia was significantly increased at these levels as well. Regarding developmental toxicity, mean fetal weight was slightly but significantly reduced at 100 and 300 mg/kg. In addition, at 300 mg/kg, there were significant increases in several skeletal variations (wavy ribs and skull, rib, and vertebral ossification delays) consistent with developmental delay. There was no evidence of either maternal or developmental toxicity at 5 or 30 mg/kg. Thus, the maternal and developmental no-observed-effect level (NOEL) was 30 mg/kg. Because developmental toxicity was observed only after administration of doses that also produced signs of maternal toxicity, 3-APN is not considered to be a selective developmental toxicant in the rat.     

INHALATION DEVELOPMENTAL TOXICITY AND REPRODUCTION STUDIES WITH CYCLOHEXANE

The reproductive and developmental toxicity of cyclohexane was assessed in a two-generation reproduction study with Crl:CD® BR rats and in developmental toxicity studies with Crl:CD®BR rats and Hra:(NZW)SPF rabbits. The animals were exposed whole-body to atmospheric concentrations of 0, 500, 2000, or 7000 ppm cyclohexane. In the two-generation reproduction study, parental effects included statistically significantly lower mean body weight, overall mean body weight gain, and overall mean food efficiency for P₁ and F₁ females of the 7000 ppm level and statistically significantly lower mean body weight for F¹ males of that level. Adult rats exposed to 2000 ppm cyclohexane and above exhibited a transient diminished or absent response to a sound stimulus while in the chambers during exposure. Mean pup weight was statistically significantly lower than control from lactation day 7 throughout the remainder of the 25-day lactation period for both F₁ and F₂ 7000 ppm litters. Changes observed at 500 ppm were either considered not to be compound related or not adverse. Therefore, the systemic-toxicity no-observed-effect level (NOEL) was 500 ppm and the reproductive NOEL was 2000 ppm. The reproductive NOEL was based solely on the decreased pup weights in both the F₁ and F₂ generations observed at 7000 ppm. In the developmental toxicity studies, only the rats showed evidence of maternal toxicity. For rats in the 7000 ppm group, statistically significant reductions were observed in overall maternal body weight gain and overall maternal food consumption for the treatment period. Rats exposed to 2000 ppm cyclohexane and above again exhibited a transient diminished or absent response to a sound stimulus while in the chambers during exposure. Therefore, for rats, the maternal no-observed-effect level (NOEL) was 500 ppm. In the rabbit developmental toxicity study, no compound-related maternal effects were observed at concentration levels of 7000 ppm and below. Therefore, the maternal NOEL for rabbits was 7000 ppm. No compound-related evidence of developmental toxicity was observed at any test concentration in either species. Therefore, the developmental NOEL for both species was 7000 ppm, the highest concentration tested.     

Developmental toxicities of methacrylic acid, ethyl methacrylate, n-butyl methacrylate, and allyl methacrylate in rats following inhalation exposure.

The developmental toxicities of 4 methacrylates were studied in Sprague-Dawley rats after inhalation exposure for 6 h/day, during days 6 to 20 of gestation. The exposure concentrations were, for methacrylic acid, 0, 50, 100, 200, or 300 ppm; for ethyl methacrylate, 0, 600, 1200, 1800, or 2400 ppm; for n-butyl methacrylate, 0, 100, 300, 600, or 1200 ppm; and for allyl methacrylate, 0, 12, 25, 50, or 100 ppm. No significant increases in embryo/fetal lethality or fetal malformations were observed after exposure to any of these methacrylates. Fetal toxicity evidenced by statistically significant decreases in fetal body weights was observed at exposure levels > or = 1200 ppm ethyl methacrylate, > or = 600 ppm n-butyl methacrylate, and at 100 ppm allyl methacrylate. Statistically significant increases in the incidence of fetuses with skeletal variations and of fetuses with any variations were noted at 1200 ppm n-butyl methacrylate. These developmental effects were observed in the presence of overt signs of maternal toxicity. While maternal toxicity was observed, methacrylic acid caused no evidence of developmental toxicity up to 300 ppm.     

Developmental toxicities of ethylbenzene, ortho-, meta-, para-xylene and technical xylene in rats following inhalation exposure.

The developmental toxicities of ethylbenzene, o-, m-, p-xylene and technical xylene were studied in Sprague-Dawley rats after inhalation exposure. Animals were exposed to either of these agents at 100, 500, 1000 or 2000 ppm, for 6 h/day, during days 6-20 of gestation. All the agents tested caused maternal toxicity expressed as a reduction in maternal body weight gain at 1000 and 2000 ppm. Decreased corrected weight gain and food consumption were observed at 1000 and 2000 ppm ethylbenzene, o-, m- or p-xylene, and at 2000 ppm technical xylene. No evidence of teratogenic effects was found after exposure to any of these agents up to 2000 ppm. Fetal toxicity evidenced by significant decreases in fetal body weights occurred at concentrations of 500 ppm or greater of o-xylene or technical xylene, and 1000 ppm or greater of ethylbenzene, m- or p-xylene. A significant increase in the mean percentage of fetuses per litter with skeletal variations was also noted at 2000 ppm ethylbenzene, o- and p-xylene. In summary, all tested agents produced developmental toxicity at 1000 and 2000 ppm, concentrations that also produced significant maternal toxicity. With o-xylene and technical xylene, developmental toxicity also occurred at 500 ppm, in the absence of maternal toxic effects. However, the only indication of a treatment-related effect was a slight decrease in fetal weight.     

Developmental toxicity study of tetramethylurea (TMU) in rats.

The developmental toxicity of tetramethylurea (TMU) was assessed in rats by inhalation exposure of the test material over days 6-20 of gestation. Groups of 25 mated female Crl:CD BR rats were exposed whole-body for 6 hours/day to concentrations of either 0, 2, 20 or 100 ppm TMU. The dams were euthanized on day 21 and the offspring were weighted, sexed, and examined for external, visceral, and skeletal alterations. Maternal toxicity was demonstrated at both 20 and 100 ppm. Maternal body weights, weight changes, and food consumption were statistically significantly reduced at these concentrations; effects were more pronounced at 100 ppm. There was evidence of developmental toxicity only at 100 ppm. The only finding was a decrease in mean fetal weight. No fetal malformations or variations occurred in fetuses derived from rats exposed to all 3 test concentrations (up to 100 ppm). The maternal no-observed-effect-level (NOEL) was 2 ppm, the fetal NOEL was 20 ppm. Thus, TMU was not considered to be uniquely toxic to the rat conceptus.     

DEVELOPMENTAL TOXICITY STUDY OF TETRAMETHYLUREA (TMU) IN RATS

The developmental toxicity of tetramethylurea (TMU) was assessed in rats by inhalation exposure of the test material over days 6–20 of gestation. Groups of 25 mated female Crl:CD®BR rats were exposed whole-body for 6 hours/day to concentrations of either 0, 2, 20 or 100 ppm TMU. The dams were euthanized on day 21 and the offspring were weighed, sexed, and examined for external, visceral, and skeletal alterations. Maternal toxicity was demonstrated at both 20 and 100 ppm. Maternal body weights, weight changes, and food consumption were statistically significantly reduced at these concentrations; effects were more pronounced at 100 ppm. There was evidence of developmental toxicity only at 100 ppm. The only finding was a decrease in mean fetal weight. No fetal malformations or variations occurred in fetuses derived from rats exposed to all 3 test concentrations (up to 100 ppm). The maternal no-observed-effect-level (NOEL) was 2 ppm, the fetal NOEL was 20 ppm. Thus, TMU was not considered to be uniquely toxic to the rat conceptus.     

Relative developmental toxicities of acrylates in rats following inhalation exposure.

The developmental toxicities of seven acrylates were studied in Sprague-Dawley rats after inhalation exposure for 6 h/day, during days 6 to 20 of gestation. The exposure concentrations were: for acrylic acid, 50, 100, 200, or 300 ppm; for methyl acrylate, 25, 50, or 100 ppm; for ethyl acrylate, 25, 50, 100, or 200 ppm; for butyl acrylate, 100, 200, or 300 ppm; for ethylhexyl acrylate, 50, 75, or 100 ppm; for hydroxyethyl acrylate, 1, 5, or 10 ppm; and for hydroxypropyl acrylate, 1, 5, or 10 ppm. No treatment-related increases in embryo/fetal mortality or fetal malformations were observed after exposure to any of these acrylates. Fetal toxicity, indicated by reduced fetal body weight, was observed after exposure to 300 ppm acrylic acid, 100 ppm methyl acrylate, 200 ppm ethyl acrylate, and 200 or 300 ppm butyl acrylate in the presence of overt signs of maternal toxicity. While there was evidence of maternal toxicity, no significant developmental toxic effects were observed after exposure to ethylhexyl acrylate, hydroxyethyl acrylate, or hydroxypropyl acrylate at any concentration. These results indicate that inhaled acrylic acid, methyl acrylate, ethyl acrylate, butyl acrylate, ethylhexyl acrylate, hydroxyethyl acrylate, and hydroxypropyl acrylate are not selectively toxic to the embryo or fetus.     

Developmental toxicity of dimethylformamide in the rat following inhalation exposure.

Dimethylformamide (DMF) is a widely used industrial solvent. DMF has been reported to be a developmental toxin when given to rodents by injection or following dermal administration. In this study, groups of pregnant rats were exposed by inhalation to either 0 (control), 30, or 300 ppm DMF from gestation day 6 through 15. In the 300 ppm rats, both maternal weight gain during gestation and fetal weights were lower than those of the controls. Fetal resorptions were not increased in this group. No significant differences among either maternal or fetal rats were seen in the 30 ppm group compared to controls. Both fetal and maternal toxicity were noted at 300 ppm and the no observed effect level under these experimental conditions was 30 ppm for both the dams and the conceptuses. DMF did not produce malformations in the rat fetus even at a level that was toxic to the dam.     

Developmental and reproductive toxicity evaluation of toluene vapor in the rat II. Developmental toxicity

The developmental toxicity of toluene was evaluated via whole body inhalation exposure, in pregnant Sprague Dawley rats exposed to toluene (99.9% pure) from gestation day (GD) 6–15 inclusive, 6 h/day, at concentrations of 0, 250, 750, 1500 and 3000 ppm (0, 938, 2812, 5625 and 11250 mg/m³). Doses were selected from a preliminary study performed over a range of concentrations from 0 to 5000 ppm, in which maternal and fetal toxicity were observed at 2000 ppm and above. This study has been cited in various regulatory documents and is presented here to allow greater accessibility to results and conclusions.

Toluene induced clinical signs in pregnant dams (ataxia, hyper-responsivity, increased water intake, decreased food consumption) at 3000 ppm, ataxia and hyper-responsivity at 1500 ppm, and reduced maternal body weight gain at 1500 during the exposure period only and at 3000 ppm from initiation of exposure to GD20. At Caesarean section on GD20, no adverse effects on implantation, number and viability of fetuses, or fetal sex distribution were observed. Litter weight and mean fetal weight was reduced at 3000 ppm and mean fetal weight was reduced at 1500 ppm. Instances of reduced or unossified skeletal elements occurred at the same dose levels. Mean fetal weight was also reduced at 250 ppm but not at 750 ppm. Extensive statistical analysis of fetal body weight data support the conclusion that there is no toxicologically significant dose-related effect on fetal body weight at or below 750 ppm. Low incidences (≤2.5%) of various malformations occurred in the 250, 1500, and 3000 ppm groups; there was no increase in the incidence of specific or total malformations with increased exposure and thus these were not attributed to toluene.

In this Toluene study, the maternal toxicity NOAEL was 750 ppm with a defined maternal and developmental toxicity LOAEL of 1500 ppm.     

Developmental toxicity study of dimethylpiperidone

The potential maternal and developmental toxicity of dimethylpiperidone (DMPD) was assessed in rats. Groups of 25 mated female Crl:CD (SD)IGS BR rats were exposed by inhalation (whole-body exposures) for approximately six hours per day over days 7-21 of gestation (G); day 1G was the day of copulation plug detection. The exposure levels were 0, 52, 260, or 340 (vapor plus aerosol) mg/m3 DMPD. During the in-life portion, body weights, food consumption, and clinical observation data were collected. On day 22G, the dams were euthanized and examined for gross external and internal alterations. The uterine contents were described and the fetuses were weighed and examined for external, visceral, and skeletal alterations. Maternal toxicity was seen at both 260 and 340 mg/m3. At 340 mg/m3, evidence of maternal toxicity included mortality, increased clinical observations, and decreased body weight and food consumption. At 260 mg/m3, maternal toxicity was limited to increased clinical observations and decreased food consumption. Developmental toxicity was also produced at 260 and 340 mg/m3. At 340 mg/m3, evidence of developmental toxicity included decreased fetal weight, increased embryofetal lethality with concomitant reductions in litter size, and increased fetal malformations and variations. At 260 mg/m3, effects in fetuses were limited to slightly decreased fetal weight and increased fetal variations; additionally, one litter from this level consisted entirely of resorptions. There were no compound-related effects in either dams or fetuses at 52 mg/m3. It was, therefore, concluded that DMPD was not selectively toxic to the rat conceptus.     

Developmental toxicity of N-methyl-2-pyrrolidone in rats following inhalation exposure.

The developmental toxicity of inhaled N-methyl-2-pyrrolidone (NMP) was studied in Sprague-Dawley rats. Pregnant rats were exposed whole body to NMP vapours at concentrations of 0, 30, 60 and 120 ppm, 6 h/day, on gestational days (GD) 6 through 20. Maternal body weight gain was significantly decreased at 60 and 120 ppm on GD 6-13 and maternal food consumption was reduced at 120 ppm on GD 13-21. No significant difference in the gestational weight change corrected for the weight of the gravid uterus was observed, whatever NMP concentration. There were no adverse effects on embryo/fetal viability or evidence of teratogenicity at any concentration tested. Fetal toxicity indicated by reduced fetal weight was observed at 120 ppm. Thus, the no-observed-adverse-effect level (NOAEL) for maternal and developmental toxicity was 30 and 60 ppm, respectively.     

Developmental toxic effects of ethylbenzene or toluene alone and in combination with butyl acetate in rats after inhalation exposure

First, the developmental toxic potential of n-butyl acetate (BA) was examined in Sprague-Dawley rats following whole body inhalation exposure, 6 h day(-1), from day 6 to 20 of gestation, at concentrations of 0, 500, 1000, 2000 and 3000 ppm. Maternal toxicity was evidenced by significant decreases in body weight gain at 2000 and 3000 ppm, and by reduced food consumption at 1000 ppm and higher concentrations. The effects on prenatal development were limited to a significant decrease in fetal weight at 3000 ppm. Thus, inhaled BA was not a selective developmental toxicant. In the second part of this study, the developmental toxic effects of simultaneous exposures to ethylbenzene (EB) and BA, or to toluene (TOL) and BA were evaluated. Pregnant rats were administered EB (0, 250 or 1000 ppm) and BA (0, 500 or 1500 ppm), or TOL (0, 500 or 1500 ppm) and BA (0, 500, 1500 ppm), separately and in combinations, using a 2 x 2 factorial design. The maternal weight gain was reduced after exposure to 1000 ppm EB, to 1500 ppm BA, or to 1500 ppm TOL, either alone or in binary combinations. A significant reduction of fetal weight was associated with exposure to 1000 ppm EB alone, to either mixtures of EB with BA, or to 1500 ppm TOL alone or combined with BA at either concentration. No embryolethal or teratogenic effects were observed whatever the exposure. There was no evidence of interaction between EB and BA or between TOL and BA in causing maternal or developmental effects.     

Developmental toxicity study of chlorpyrifos in rats

Chlorpyrifos (O,O-diethyl-O-(3,5,6-trichloro-2-pyridyl)-phosphorothioate) was evaluated for potential developmental toxicity. Groups of 30 bred female Fischer 344 rats were given 0, 5, 15, and 25mg/kg per day by gavage on gestation days 6-15; the fetuses were evaluated on gestation day 21. Clinical signs of toxicity attributed to chlorpyrifos were noted in dams receiving 15 and 25mg/kg per day. Maternal effects in these groups also included depressed body weight and acetylcholinesterase activity. Fetal weight and viability were decreased, and fetal death and early resorption were increased at the 25mg/kg per day maternal dose. Visceral, skeletal, and external variations were also increased in this group. Chlorpyrifos showed fetotoxic and teratogenic effects at a maternal dose of 25mg/kg per day, a dose that also produced maternal toxicity.     

Developmental toxicity evaluation of unleaded gasoline vapor in the rat.

To evaluate the potential of unleaded gasoline vapor for developmental toxicity, a sample was prepared by slowly heating API 94-02 (1990 industry average gasoline) and condensing the vapor. The composition of this vapor condensate, which comprises 10.4% by volume of the starting gasoline, is representative of real-world exposure to gasoline vapor encountered at service stations and other occupational settings and consists primarily of volatile short chain (C4-C6) aliphatic hydrocarbons (i.e. paraffins) with small amounts of cycloparaffins and aromatic hydrocarbons. A preliminary study in rats and mice resulted in no developmental toxicity in either species. However, a slight reduction in maternal body weight gain in rats led to the selection of rats for this guideline study. Groups of pregnant rats (n = 24/group) were exposed to unleaded gasoline vapor at concentrations of 0, 1000, 3000, or 9000 (75% lower explosive limit) ppm equivalent to 0, 2653, 7960, or 23,900 mg/m3, for 6 h/day on gestation days 6-19. All rats were sacrificed on gestation day 20. No maternal toxicity was observed. Developmentally, there were no differences between treated and control groups in malformations, total variations, resorptions, fetal body weight, or viability. The maternal and developmental NOAEL is 9000 ppm. Under conditions of this study, unleaded gasoline vapors did not produce evidence of developmental toxicity.     

Relative Developmental Toxicities of Inhaled Aliphatic Mononitriles in Rats

The developmental toxicities of eight aliphatic raononitrileswere studied in Sprague-Dawley rats after inhalation exposurefor 6 hr/day, during Days 6 to 20 of gestation. The range ofexposure 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 methacryloni-trile, 12to 100 ppm; for allylnitrile 12 to 50 ppm; and for 2-chloroacrylonitrile,1 to 12 ppm. Embryolethality was observed after exposure to1800 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 theabsence of significant maternal toxicity, allylnitrile causedembryolethality, fetotoxicity, and clear teratogenicity at 50ppm, and n-butyronitrile and methacrylonitrile caused fetotoxicityat 200 ppm and 100 ppm, respectively. While maternal toxicitywas observed for 2-chloroacrylonitrile, it did not cause significantembryonal or fetal toxicity up to 12 ppm.     

Reproductive and developmental toxicity of inhaled 2,3-dichloro-1,3-butadiene in rats

Inhalation developmental and reproductive toxicity studies were conducted with 2,3-dichloro-1,3-butadiene (DCBD), a monomer used in the production of synthetic rubber. In the reproductive toxicity study, Crl:CD^®(SD)IGS BR rats (24/sex/group) were exposed whole body by inhalation to 0, 1, 5, or 50 ppm DCBD (6 h/day) for approximately 10–11 weeks total, through premating (8 weeks; 5 days/week), cohabitation of mating pairs (up to 2 weeks, 7 days/week), post-cohabitation for males (7 days) and from conception to implantation (gestation days 0–7 [GD 0–7]), followed by a recovery period (GD 8–21) for presumed pregnant females. Estrous cyclicity was evaluated during premating (last 3 weeks) and cohabitation. Reproductive organs and potential target organs, sperm parameters, and GD 21 fetuses (viability, weight, external alterations) were evaluated. In the developmental study, pregnant Crl:CD^®(SD)IGS BR rats (22/group) were exposed whole body by inhalation to 0, 1, 10, or 50 ppm DCBD (6 h/day) on GD 6–20; dams were necropsied on GD 21 (gross post-mortem only) and fetuses were evaluated (viability, weight, and external, visceral and skeletal exams). During the in-life portion of the studies, body weight, food consumption, and clinical observation data were collected. At 50 ppm, gasping and labored breathing occurred in both studies during the first few exposures; body weight and food consumption parameters were affected in parental animals from both studies, but were more severely affected in the developmental study. Fetal weight was decreased in the developmental study at 50 ppm. Degeneration of the nasal olfactory epithelium was observed in the reproduction study at 50 ppm. There were no effects on reproductive function, embryo–fetal viability, or increases in fetal structural alterations in either study. The no-observed-adverse-effect level (NOAEL) for reproductive toxicity was 50 ppm. The NOAEL for systemic toxicity in the reproduction study was 5 ppm based on adverse effects on body weight and food consumption parameters and nasal olfactory epithelial toxicity at 50 ppm in parental rats. The NOAEL for maternal and developmental toxicity was 10 ppm based on reduced maternal weight gain and food consumption and reduced fetal weight at 50 ppm in the developmental toxicity study.