Tyl R W, Pritts I M, France K A, Fisher L C, Tyler T R
Bushy Run Research Center, Export, Pennsylvania 15632.
Fundam Appl Toxicol. 1988 Jan;10(1):20-39. doi: 10.1016/0272-0590(88)90248-5.
Pregnant Fischer 344 rats and New Zealand white rabbits were exposed to 2-ethoxyethanol acetate (EEA; CAS No. 111-15-9) vapor by inhalation on Gestational Days 6 through 15 (rats) or 6 through 18 (rabbits) at concentrations of 0, 50, 100, 200, or 300 ppm, 6 hr/day. The animals were terminated on Gestational Day 21 (rats) or 29 (rabbits) and fetuses were examined for external, visceral, and skeletal malformations and variations. In rabbits, exposure to 100-300 ppm resulted in maternal toxicity: decreased weight gain at 100-300 ppm, clinical signs at 200-300 ppm, alterations in hematology at 100-300 ppm, reduced gravid uterine weight at termination at 200-300 ppm, and elevated absolute liver weight at 300 ppm. Developmental toxicity was observed at 100-300 ppm: an increased incidence of totally resorbed litters at 200-300 ppm, an increase in nonviable fetuses at 300 ppm, and a decrease in viable implants (live fetuses) per litter at 200-300 ppm. The incidence of fetal malformations (external, visceral, and skeletal) was increased at 200-300 ppm. The incidence of total malformations was 100% at 300 ppm and significantly increased at 200 ppm. Reduced fetal ossification was observed at 100-300 ppm. In rats, exposure to 100-300 ppm also resulted in maternal toxicity: reduced weight gain and reduced food consumption at 200-300 ppm and elevated relative liver weight and alterations in hematology at 100-300 ppm. Absolute maternal liver weight was increased at all EEA exposure concentrations; relative liver weight was increased at 100-300 ppm. Developmental toxicity was observed at 100-300 ppm: increased nonviable implantations/litter (300 ppm), reduced fetal body weight/litter (200-300 ppm), and increased incidence of external (300 ppm), visceral, and skeletal (100-300 ppm) variations indicative of toxicity. The incidence of visceral, skeletal, and total malformations was increased at 200-300 ppm. In conclusion, in both species, inhalation exposure to EEA during organogenesis produced maternal toxicity at 100-300 ppm and developmental toxicity at 100-300 ppm, including teratogenicity at 200-300 ppm. At 50 ppm in both species, there was no evidence of maternal or developmental toxicity, including teratogenicity.
将妊娠的Fischer 344大鼠和新西兰白兔在妊娠第6至15天(大鼠)或第6至18天(兔子)通过吸入方式暴露于乙酸2-乙氧基乙酯(EEA;化学物质登记号:111-15-9)蒸气中,浓度分别为0、50、100、200或300 ppm,每天暴露6小时。在妊娠第21天(大鼠)或第29天(兔子)处死动物,检查胎儿的外观、内脏和骨骼畸形及变异情况。在兔子中,暴露于100 - 300 ppm会导致母体毒性:100 - 300 ppm时体重增加减少,200 - 300 ppm时有临床症状,100 - 300 ppm时血液学指标改变,200 - 300 ppm时处死时妊娠子宫重量减轻,300 ppm时肝脏绝对重量增加。在100 - 300 ppm观察到发育毒性:200 - 300 ppm时完全吸收胎仔的发生率增加,300 ppm时非存活胎儿数量增加,200 - 300 ppm时每窝存活植入物(活胎)数量减少。200 - 300 ppm时胎儿畸形(外观、内脏和骨骼)的发生率增加。300 ppm时总畸形发生率为100%,200 ppm时显著增加。在100 - 300 ppm观察到胎儿骨化减少。在大鼠中,暴露于100 - 300 ppm也导致母体毒性:200 - 300 ppm时体重增加减少和食物摄入量减少以及100 - 300 ppm时肝脏相对重量增加和血液学指标改变。所有EEA暴露浓度下母体肝脏绝对重量均增加;100 - 300 ppm时肝脏相对重量增加。在100 - 300 ppm观察到发育毒性:300 ppm时每窝非存活植入物增加,200 - 300 ppm时每窝胎儿体重减轻,300 ppm时外观变异增加,100 - 300 ppm时内脏和骨骼变异增加,提示有毒性。200 - 300 ppm时内脏、骨骼和总畸形的发生率增加。总之,在两个物种中,器官形成期吸入EEA在100 - 300 ppm时产生母体毒性,在100 - 300 ppm时产生发育毒性,包括200 - 300 ppm时的致畸性。在两个物种中,50 ppm时均无母体或发育毒性证据,包括致畸性。