NTP technical report on the toxicity studies of Ethylene Glycol Ethers: 2-Methoxyethanol, 2-Ethoxyethanol, 2-Butoxyethanol (CAS Nos. 109-86-4, 110-80-5, 111-76-2) Administered in Drinking Water to F344/N Rats and B6C3F1 Mice.

Toxicity report series Pub Date : 1993-07-01
M. Dieter
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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.</p>","PeriodicalId":23116,"journal":{"name":"Toxicity report series","volume":"26 ","pages":"1-G15"},"PeriodicalIF":0.0000,"publicationDate":"1993-07-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Toxicity report series","FirstCategoryId":"1085","ListUrlMain":"","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 0

Abstract

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.

2-甲氧基乙醇,2-乙氧基乙醇,2-丁氧基乙醇(CAS编号109-86- 4,110 -80- 5,111 -76-2)在饮用水中对F344/N大鼠和B6C3F1小鼠的毒性研究的NTP技术报告。
乙二醇烷基醚是一类大批量生产的化学品,作为溶剂和化学中间体在工业上有着广泛的应用。在为期2周和13周的饮用水研究中,对F344/N大鼠和B6C3F1小鼠进行了三种乙二醇醚、2-甲氧基乙醇、2-乙氧基乙醇和2-丁氧基乙醇的毒性比较研究。在动物中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。遗传毒性也被评估为每个乙二醇醚在几个体外和体内的分析。在为期两周的研究中,每组5只雄性和5只雌性大鼠和小鼠在饮用水中加入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用水量估算,2-甲氧基乙醇的化合物消耗量为100至400毫克/千克,2-乙氧基乙醇为200至1600毫克/千克,2-丁氧基乙醇为70至300毫克/千克。对于小鼠,2-甲氧基乙醇的消耗值为200至1300毫克/公斤,2-乙氧基乙醇为400至2800毫克/公斤,2-丁氧基乙醇为90至1400毫克/公斤。在为期两周的研究中,对大鼠或小鼠的生存没有化学相关的影响。用2-甲氧基乙醇或2-乙氧基乙醇治疗两周后,雄性和雌性大鼠的体重增加都有所减少,而且用乙二醇醚治疗两种性别的大鼠的饮水量都有剂量相关的减少。除接受2-甲氧基乙醇或2-乙氧基乙醇治疗的雄性和雌性大鼠胸腺萎缩和雄性大鼠睾丸萎缩外,用乙二醇醚治疗的大鼠和小鼠器官重量的变化大多是偶发性的(小鼠)或与较低的最终平均体重(大鼠)有关。在为期13周的大鼠研究中,每组10只雄性和10只雌性分别在饮用水中加入浓度为750至6000 ppm、1250至20,000 ppm或750至6000 ppm的2-甲氧基乙醇、2-乙氧基乙醇或2-丁氧基乙醇。在为期13周的小鼠研究中,每组10只雄性和10只雌性分别在饮用水中加入浓度为2000至10,000 ppm、2500至40,000 ppm或750至6000 ppm的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用水量估算,2-甲氧基乙醇的化合物消耗量为70至800毫克/千克,2-乙氧基乙醇为100至2200毫克/千克,2-丁氧基乙醇为70至500毫克/千克。对于小鼠,2-甲氧基乙醇的消耗值为300至1800毫克/公斤,2-乙氧基乙醇为600至11000毫克/公斤,2-丁氧基乙醇为100至1300毫克/公斤。化学相关的死亡发生在雄性和雌性大鼠中,剂量为4500 ppm或6000 ppm的2-甲氧基乙醇,雄性和雌性大鼠中剂量为20,000 ppm的2-乙氧基乙醇。给药2-丁氧基乙醇的大鼠和给药2-甲氧基乙醇、2-乙氧基乙醇或2-丁氧基乙醇的小鼠均未发生死亡。在所有三项研究中,给药的大鼠和小鼠体重增加都有所减少;2-甲氧基乙醇对体重增加的减少最大。在给予2-甲氧基乙醇或2-乙氧基乙醇的大鼠中,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精小管中生殖上皮的剂量相关性变性比2-乙氧基乙醇处理的大鼠更严重。在对雄性大鼠进行的特殊停止暴露研究中,在60天后停止给药乙二醇醚,用3000 ppm的2-甲氧基乙醇处理的大鼠的精小管出现明显的变性,用1500 ppm处理的大鼠观察到轻度至中度变性。用10,000或20,000 ppm的2-乙氧基乙醇处理的大鼠出现中度至明显的睾丸变性,但用5000 ppm处理的大鼠则没有。用这些药物治疗30天和56天后,仅观察到睾丸变性部分恢复。用1500 ~ 6000 ppm的2-丁氧基乙醇处理60天后,没有睾丸变性。2-甲氧基乙醇治疗13周导致进行性贫血,伴有骨髓细胞耗竭和脾囊纤维化。使用2-乙氧基乙醇也会出现贫血,但骨髓、脾脏和肝脏的造血能力增加表明了适应性反应的证据。2-丁氧基乙醇的毒性仅限于肝脏和造血系统。雌雄大鼠的肝脏均出现细胞质改变和轻微的肝细胞变性。轻度贫血,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(仅限雌性)有相似的影响。 2-甲氧基乙醇比2-乙氧基乙醇对睾丸精小管生殖上皮的剂量相关性变性更严重。使用2-甲氧基乙醇时,脾造血功能的剂量相关性增加也更为明显。2-甲氧基乙醇和2-乙氧基乙醇均引起雌性小鼠肾上腺x区显著的脂质空泡化。在小鼠中,没有化学相关的病变归因于2-丁氧基乙醇。所有三种乙二醇醚在鼠伤寒沙门菌突变试验中均为阴性,该试验用和不用诱导的仓鼠和大鼠肝脏S9进行。在小鼠淋巴瘤L5178Y细胞突变实验中,2-乙氧基乙醇在没有S9的情况下呈阴性,但在有诱导的大鼠肝脏S9的情况下呈弱阳性;2-甲氧基乙醇和2-丁氧基乙醇未在本试验中检测。高浓度2-乙氧基乙醇诱导含S9和不含S9的中国仓鼠卵巢细胞的姐妹染色单体交换(ses)。2-乙氧基乙醇也可诱导染色体畸变(Abs),但仅在缺乏S9且细胞周期不延迟的情况下。相比之下,2-丁氧基乙醇诱导细胞周期延迟,但不诱导sce或不含S9的抗体。2-乙氧基乙醇是唯一一种在果蝇生殖细胞中诱导性别连锁隐性致死突变的乙二醇醚;饲养试验和注射试验均为阴性。综上所述,基于生存、体重增加减少和组织病理学效应,三乙二醇烷基醚的毒性等级为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。在对大鼠进行的为期13周的2-甲氧基乙醇研究中,没有达到未观察到的不良反应水平(NOAEL),因为在最低浓度(750 ppm)下,雄性睾丸变性和雄性和雌性胸腺重量下降。在对大鼠进行为期13周的2-乙氧基乙醇研究中,雄性胸腺重量减少的NOAEL为1250 ppm;雌性大鼠经2-乙氧基乙醇处理13周后,所有组织病理学和血液学影响的NOAEL为5000ppm。在用2-丁氧基乙醇治疗13周的大鼠中,雄性和雌性肝脏变性的NOAEL为1500 ppm。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没有达到NOAEL,因为在最低浓度(2000ppm)下,肾上腺肥大和脾脏造血功能增加。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20,000 ppm。在为期13周的2-乙氧基乙醇研究中,雌性小鼠肾上腺肥大和脾脏造血功能增加的NOAEL为5000 ppm。在以高达6000 ppm的浓度给雄性或雌性小鼠13周的时间里,没有发现明显的化学相关影响。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;甲基纤维素;2-丁氧基乙醇:乙二醇单丁醚;丁基甲基纤维素。
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