Dieter M.
Toxic Rep Ser. 1993 Jul;26:1-G15.
Glycol alkyl ethers represent a class of high-production-volume chemicals with widespread industrial applications as solvents and chemical intermediates. Comparative toxicity studies with three glycol ethers, 2-methoxyethanol, 2-ethoxyethanol, and 2-butoxyethanol, were conducted in F344/N rats and B6C3F1 mice in both 2-week and 13-week drinking water studies. Toxicologic endpoints evaluated in animals included histopathology, hematology, clinical chemistry, urinalysis, and reproductive system parameters. Genetic toxicity was also evaluated for each glycol ether in several in vitro and in vivo assays. In the 2-week studies, groups of five male and five female rats and mice received 2-methoxyethanol, 2-ethoxyethanol, or 2-butoxyethanol in the drinking water. Estimates of compound consumption based on water consumption by male and female rats ranged from 100 to 400 mg/kg for 2-methoxyethanol, 200 to 1600 mg/kg for 2-ethoxyethanol, and 70 to 300 mg/kg for 2-butoxyethanol. For mice, consumption values ranged from 200 to 1300 mg/kg for 2-methoxyethanol, 400 to 2800 mg/kg for 2-ethoxyethanol, and 90 to 1400 mg/kg for 2-butoxyethanol. There were no chemical-related effects on survival for rats or mice in the 2-week studies. Decreased body weight gains were noted for both male and female rats treated with 2-methoxyethanol or 2-ethoxyethanol for 2 weeks, and there were dose-related decreases in water consumption for rats of each sex treated with the ethylene glycol ethers. Most of the changes in organ weights for rats and mice treated with the glycol ethers were sporadic (mice) or related to low final mean body weights (rats), except for thymic atrophy in male and female rats and testicular atrophy in males of both species receiving 2-methoxyethanol or 2-ethoxyethanol. In the 13-week studies in rats, groups of 10 males and 10 females received 2-methoxyethanol, 2-ethoxyethanol, or 2-butoxyethanol in the drinking water at concentrations ranging from 750 to 6000 ppm, 1250 to 20,000 ppm, or 750 to 6000 ppm, respectively. In the 13-week studies in mice, groups of 10 males and 10 females received 2-methoxyethanol, 2-ethoxyethanol, or 2-butoxyethanol in the drinking water at concentrations ranging from 2000 to 10,000 ppm, 2500 to 40,000 ppm, or 750 to 6000 ppm, respectively. Estimates of compound consumption based on water consumption by male and female rats ranged from 70 to 800 mg/kg for 2-methoxyethanol, 100 to 2200- mg/kg for 2-ethoxyethanol, and 70 to 500 mg/kg for 2-butoxyethanol. For-mice, consumption values ranged from 300 to 1800 mg/kg for 2-methoxyethanol, 600 to 11,000 mg/kg for 2-ethoxyethanol, and 100 to 1300 mg/kg for 2-butoxyethanol. Chemical-related mortality occurred in male and female rats administered 4500 or 6000 ppm 2-methoxyethanol and in male and female rats administered 20,000 ppm 2-ethoxyethanol. No deaths occurred in rats administered 2-butoxyethanol or in mice administered 2-methoxyethanol, 2-ethoxyethanol, or 2-butoxyethanol. Decreased body weight gains occurred in dosed rats and mice in all three studies; the greatest reductions in body weight gain were seen with 2-methoxyethanol. In rats administered 2-methoxyethanol or 2-ethoxyethanol, treatment-related histopathologic changes were observed in the testes, thymus, and hematopoietic tissues (spleen, bone marrow, and liver). A dose-related degeneration of the germinal epithelium in the seminiferous tubules of the testes was more severe in 2-methoxyethanol-treated rats than in rats treated with 2-ethoxyethanol. In special stop-exposure studies in male rats in which administration of the glycol ethers was stopped after 60 days, marked degeneration of the seminiferous tubules was present in rats treated with 3000 ppm 2-methoxyethanol, and mild to moderate degeneration was observed in rats treated with 1500 ppm. Moderate to marked testicular degeneration was present in rats treated with 10,000 or 20,000 ppm 2-ethoxyethanol but not in rats treated with 5000 ppm. After 30 and 56 days of recovery from treatment with these chemicals, only partial recovery from testicular degeneration was observed. There was no testicular degeneration after 60 days of treatment with 1500 to 6000 ppm 2-butoxyethanol. 2-Methoxyethanol treatment for 13 weeks resulted in a progressive anemia associated with a cellular depletion of bone marrow and fibrosis of the splenic capsule. Anemia was also seen with 2-ethoxyethanol, but evidence of an adaptive response was indicated by increased hematopoiesis in the bone marrow, spleen, and liver. Toxicity with 2-butoxyethanol was limited to the liver and hematopoietic system. Cytoplasmic alteration and a minimal hepatocellular degeneration were present in the liver of male and female rats. A minimal anemia was present, and a hematopoietic response was evident in the bone marrow and spleen. In mice, 2-methoxyethanol and 2-ethoxyethanol had similar effects on the testes, spleen, and adrenal gland (females only). A dose-related degeneration of the germinal epithelium in seminiferous tubules of the testes was more severe with 2-methoxyethanol than with 2-ethoxyethanol. A dose-related increase in splenic hematopoiesis was also more prominent with 2-methoxyethanol. Both 2-methoxyethanol and 2-ethoxyethanol caused a prominent lipid vacuolization of the X-zone of the adrenal gland in female mice. There were no chemical-related lesions attributed to 2-butoxyethanol administration in mice. All three of the glycol ethers were negative in Salmonella typhimurium mutation tests conducted with and without induced hamster and rat liver S9. In the mouse lymphoma L5178Y cell mutation assay, 2-ethoxyethanol was negative without S9 but was weakly positive in the presence of induced rat liver S9; 2-methoxyethanol and 2-butoxyethanol were not tested in this assay. At high concentrations, 2-ethoxyethanol induced sister chromatid exchanges (SCEs) in Chinese hamster ovary cells with and without S9. Chromosomal aberrations (Abs) were also induced by 2-ethoxyethanol, but only in the absence of S9 and without a delay in cell cycle. In contrast, 2-butoxyethanol induced cell cycle delay but did not induce SCEs or Abs with or without S9. 2-Ethoxyethanol was the only glycol ether tested for induction of sex-linked recessive lethal mutations in germ cells of Drosophila melanogaster; both feeding and injection trials were negative. In summary, based on survival, decreased body weight gains, and histopathologic effects, the rank order of toxicity for the three glycol alkyl ethers was 2-methoxyethanol>2-ethoxyethanol>2-butoxyethanol; the toxic effects were more severe in rats than in mice. In the 13-week study of 2-methoxyethanol in rats, a no-observed-adverse-effect level (NOAEL) was not reached, since testicular degeneration in males and decreased thymus weights in males and females occurred at the lowest concentration administered (750 ppm). In the 13-week study of 2-ethoxyethanol in rats, the NOAEL for decreased thymus weights in males was 1250 ppm; for female rats treated with 2-ethoxyethanol for 13 weeks, the NOAEL for all histopathologic and hematologic effects was 5000 ppm. In rats treated with 2-butoxyethanol for 13 weeks, the NOAEL for liver degeneration was 1500 ppm in males and females. For male mice treated with 2-methoxyethanol for 13 weeks, the NOAEL for testicular degeneration and increased hematopoiesis in the spleen was 2000 ppm. A NOAEL was not reached for female mice treated with 2-methoxyethanol, since adrenal gland hypertrophy and increased hematopoiesis in the spleen occurred at the lowest concentration administered (2000 ppm). For male mice treated with 2-ethoxyethanol for 13 weeks, the NOAEL for testicular degeneration and increased hematopoiesis in the spleen was 20,000 ppm. For female mice in the 13-week study of 2-ethoxyethanol, the NOAEL for adrenal gland hypertrophy and increased hematopoiesis in the spleen was 5000 ppm. No clear chemical-related effects were seen in male or female mice administered 2-butoxyethanol for 13 weeks at concentrations as high as 6000 ppm. Synonyms: 2-Methoxyethanol: Ethylene glycol monomethyl ether; methyl cellosolve; 2-Ethoxyethanol: Ethylene glycol monoethyl ether; cellosolve; 2-Butoxyethanol: Ethylene glycol monobutyl ether; butyl cellosolve.
乙二醇烷基醚是一类高产量化学品,作为溶剂和化学中间体在工业上有广泛应用。在F344/N大鼠和B6C3F1小鼠中进行了为期2周和13周的饮水研究,比较了三种乙二醇醚(2-甲氧基乙醇、2-乙氧基乙醇和2-丁氧基乙醇)的毒性。对动物评估的毒理学终点包括组织病理学、血液学、临床化学、尿液分析和生殖系统参数。还通过几种体外和体内试验评估了每种乙二醇醚的遗传毒性。在为期2周的研究中,每组五只雄性和五只雌性大鼠及小鼠通过饮水摄入2-甲氧基乙醇、2-乙氧基乙醇或2-丁氧基乙醇。根据雄性和雌性大鼠的饮水量估算,2-甲氧基乙醇的化合物摄入量为100至400mg/kg,2-乙氧基乙醇为200至1600mg/kg,2-丁氧基乙醇为70至300mg/kg。对于小鼠,2-甲氧基乙醇的摄入量为200至1300mg/kg,2-乙氧基乙醇为400至2800mg/kg,2-丁氧基乙醇为90至1400mg/kg。在为期2周的研究中,大鼠和小鼠的存活情况未出现与化学物质相关的影响。用2-甲氧基乙醇或2-乙氧基乙醇处理2周的雄性和雌性大鼠体重增加减少,用乙二醇醚处理的各性别大鼠饮水量呈剂量相关减少。用乙二醇醚处理的大鼠和小鼠的大多数器官重量变化是偶发性的(小鼠)或与最终平均体重低有关(大鼠),但接受2-甲氧基乙醇或2-乙氧基乙醇的雄性和雌性大鼠出现胸腺萎缩,两种物种的雄性出现睾丸萎缩。在大鼠的13周研究中,每组10只雄性和10只雌性大鼠通过饮水摄入2-甲氧基乙醇、2-乙氧基乙醇或2-丁氧基乙醇,浓度分别为750至6000ppm、1250至20000ppm或750至6000ppm。在小鼠的13周研究中,每组10只雄性和10只雌性小鼠通过饮水摄入2-甲氧基乙醇、2-乙氧基乙醇或2-丁氧基乙醇,浓度分别为2000至10000ppm、2500至40000ppm或750至6000ppm。根据雄性和雌性大鼠的饮水量估算,2-甲氧基乙醇的化合物摄入量为70至800mg/kg,2-乙氧基乙醇为100至2200mg/kg,2-丁氧基乙醇为70至500mg/kg。对于小鼠,2-甲氧基乙醇的摄入量为300至1800mg/kg,2-乙氧基乙醇为600至11000mg/kg,2-丁氧基乙醇为100至1300mg/kg。给予4500或6000ppm 2-甲氧基乙醇的雄性和雌性大鼠以及给予20000ppm 2-乙氧基乙醇的雄性和雌性大鼠出现与化学物质相关的死亡。给予2-丁氧基乙醇的大鼠或给予2-甲氧基乙醇、2-乙氧基乙醇或2-丁氧基乙醇的小鼠未出现死亡。在所有三项研究中,给药的大鼠和小鼠体重增加减少;2-甲氧基乙醇导致的体重增加减少最为明显。给予2-甲氧基乙醇或2-乙氧基乙醇的大鼠,在睾丸、胸腺和造血组织(脾脏、骨髓和肝脏)中观察到与治疗相关的组织病理学变化。2-甲氧基乙醇处理的大鼠睾丸生精小管中生发上皮的剂量相关变性比2-乙氧基乙醇处理的大鼠更严重。在雄性大鼠的特殊停止暴露研究中,给予乙二醇醚60天后停止给药,给予3000ppm 2-甲氧基乙醇的大鼠出现明显的生精小管变性,给予1500ppm的大鼠观察到轻度至中度变性。给予10000或20000ppm 2-乙氧基乙醇的大鼠出现中度至明显的睾丸变性,但给予5000ppm的大鼠未出现。用这些化学物质处理30天和56天后恢复,睾丸变性仅部分恢复。给予1500至6000ppm 2-丁氧基乙醇60天后未出现睾丸变性。2-甲氧基乙醇处理13周导致进行性贫血,伴有骨髓细胞减少和脾包膜纤维化。2-乙氧基乙醇也出现贫血,但骨髓、脾脏和肝脏中造血增加表明有适应性反应。2-丁氧基乙醇的毒性仅限于肝脏和造血系统。雄性和雌性大鼠肝脏出现细胞质改变和轻微的肝细胞变性。出现轻微贫血,骨髓和脾脏有明显的造血反应。在小鼠中,2-甲氧基乙醇和2-乙氧基乙醇对睾丸、脾脏和肾上腺(仅雌性)有类似影响。2-甲氧基乙醇处理的睾丸生精小管中生发上皮的剂量相关变性比2-乙氧基乙醇更严重。2-甲氧基乙醇处理时脾脏造血的剂量相关增加也更明显。2-甲氧基乙醇和2-乙氧基乙醇均导致雌性小鼠肾上腺X区明显的脂质空泡化。给予2-丁氧基乙醇的小鼠未出现与化学物质相关的病变。在有或无诱导的仓鼠和大鼠肝脏S9的情况下进行的鼠伤寒沙门氏菌突变试验中,所有三种乙二醇醚均为阴性。在小鼠淋巴瘤L5178Y细胞突变试验中,2-乙氧基乙醇在无S9时为阴性,但在有诱导的大鼠肝脏S9时为弱阳性;2-甲氧基乙醇和2-丁氧基乙醇未在此试验中测试。在高浓度下,2-乙氧基乙醇在有或无S9的情况下均可诱导中国仓鼠卵巢细胞中的姐妹染色单体交换(SCE)。2-乙氧基乙醇也可诱导染色体畸变(Ab),但仅在无S9且细胞周期无延迟的情况下。相比之下,2-丁氧基乙醇诱导细胞周期延迟,但在有或无S9的情况下均未诱导SCE或Ab。2-乙氧基乙醇是唯一测试其对果蝇生殖细胞中伴性隐性致死突变诱导作用的乙二醇醚;喂食和注射试验均为阴性。总之,基于存活情况、体重增加减少和组织病理学影响,三种乙二醇烷基醚的毒性顺序为2-甲氧基乙醇>2-乙氧基乙醇>2-丁氧基乙醇;大鼠的毒性作用比小鼠更严重。在大鼠中进行的2-甲氧基乙醇13周研究中,未达到无观察到有害作用水平(NOAEL),因为在给予的最低浓度(750ppm)下,雄性出现睾丸变性,雄性和雌性胸腺重量减少。在大鼠中进行的2-乙氧基乙醇13周研究中,雄性胸腺重量减少的NOAEL为1250ppm;对于用2-乙氧基乙醇处理13周的雌性大鼠,所有组织病理学和血液学影响的NOAEL为5000ppm。用2-丁氧基乙醇处理13周的大鼠,雄性和雌性肝脏变性的NOAEL为1500ppm。对于用2-甲氧基乙醇处理13周的雄性小鼠,睾丸变性和脾脏造血增加的NOAEL为2000ppm。用2-甲氧基乙醇处理的雌性小鼠未达到NOAEL,因为在给予的最低浓度(2000ppm)下出现肾上腺肥大和脾脏造血增加。对于用2-乙氧基乙醇处理13周的雄性小鼠,睾丸变性和脾脏造血增加的NOAEL为20000ppm。在2-乙氧基乙醇13周研究中,雌性小鼠肾上腺肥大和脾脏造血增加的NOAEL为5000ppm。给予浓度高达6000ppm的2-丁氧基乙醇13周的雄性或雌性小鼠未出现明显的与化学物质相关的影响。同义词:2-甲氧基乙醇:乙二醇单甲醚;甲基溶纤剂;2-乙氧基乙醇:乙二醇单乙醚;溶纤剂;2-丁氧基乙醇:乙二醇单丁醚;丁基溶纤剂。