National Toxicology Program, Research Triangle Park, NC 27709, USA.
Natl Toxicol Program Tech Rep Ser. 2011 Oct(566):1-174.
Diethylamine is used mainly as a chemical intermediate to produce the corrosion inhibitor N,N-diethylethanolamine and a lesser amount is used to produce pesticides and insect repellants and in rubber processing. Diethylamine was nominated for study by the National Institute of Environmental Health Sciences based upon its high production volume and ubiquitous natural occurrence in trace amounts and because of the lack of chronic toxicity and carcinogenicity data on the chemical. Male and female F344/N rats and B6C3F1 mice were exposed to diethylamine (approximately 99.9% pure) by inhalation for 2 weeks, 3 months, or 2 years. Genetic toxicology studies were conducted in bacterial mutagenicity tester strains and mouse peripheral blood erythrocytes. 2-WEEK STUDY IN RATS: Groups of five male and five female rats were exposed to diethylamine vapor at concentrations of 0, 31, 62.5, 125, 250, or 500 ppm, 6 hours plus T90 (12 minutes) per day, 5 days per week for 16 days. All rats survived to the end of the study. The mean body weights of 250 and 500 ppm males and females and 125 ppm males were significantly less than those of the chamber controls. Clinical findings included lethargy, nasal/eye discharge, abnormal breathing, thinness, eye abnormalities, and discolored urine. The thymus weights of males exposed to 125 ppm or greater and females exposed to 500 ppm were significantly less than those of the chamber controls. Focal eye lesions were noted at necropsy in four males and three females exposed to 500 ppm and one male exposed to 250 ppm. Crusty noses were observed in most 500 ppm males and females and in two 250 ppm males. Suppurative inflammation, necrosis of the turbinates (except in one 125 ppm female), and squamous metaplasia of the respiratory epithelium of the nose were present in all rats exposed to 125 ppm or greater. Ulcer of the respiratory epithelium and atrophy of the olfactory epithelium occurred in all rats exposed to 250 or 500 ppm, and ulcer of the nasopharyngeal duct was present in all 500 ppm rats. Suppurative inflammation of the cornea was present in most rats exposed to 500 ppm. 2-WEEK STUDY IN MICE: Groups of five male and five female mice were exposed to diethylamine vapor at concentrations of 0, 31, 62.5, 125, 250, or 500 ppm, 6 hours plus T90 (12 minutes) per day, 5 days per week for 17 days. Two males and three females exposed to 500 ppm died during the first week of the study. The mean body weights of males and females exposed to 125 ppm or greater were significantly less than those of the chamber controls. Males and females exposed to 250 or 500 ppm lost weight during the study. Lethargy, abnormal breathing, and thinness were observed in most mice exposed to 250 or 500 ppm. Eye irritation and discharge, nasal discharge, and low fecal and urine output were noted in 500 ppm mice. Thymus weights of 250 and 500 ppm males and 125 ppm or greater females were significantly less than those of the chamber controls. Suppurative inflammation of the nose occurred in all males exposed to 250 or 500 ppm and all females exposed to 125 ppm or greater, and most males exposed to 125 ppm. Turbinate necrosis occurred in all exposed mice except one 31 ppm female. Squamous metaplasia of the respiratory epithelium and olfactory epithelial atrophy were seen in mice exposed to 125 ppm or greater. In the lung, the incidence of minimal chronic active inflammation of mainstem bronchi was significantly increased in 500 ppm males. 3-MONTH STUDY IN RATS: Groups of 10 male and 10 female rats were exposed to diethylamine vapor at concentrations of 0, 8, 16, 32, 62, or 125 ppm, 6 hours plus T90 (12 minutes) per day, 5 days per week for 14 weeks. All rats survived to the end of the study. Mean body weights of all exposed groups were similar to those of the chamber control groups. There were significant exposure concentration-related decreases in sperm motility in 32, 62, and 125 ppm males; there were no significant differences in the lengths of estrous cycles between chamber control and exposed groups of females. Exposure-related nasal lesions were seen primarily in rats exposed to 62 or 125 ppm. These lesions included turbinate necrosis, suppurative inflammation, respiratory epithelial hyperplasia, squamous metaplasia of the respiratory epithelium, and olfactory epithelial atrophy. 3-MONTH STUDY IN MICE: Groups of 10 male and 10 female mice were exposed to diethylamine vapor at concentrations of 0, 8, 16, 32, 62, or 125 ppm, 6 hours plus T90 (12 minutes) per day, 5 days per week for 14 weeks. All mice survived to the end of the study. The mean body weights of 125 ppm males and females were significantly less than those of the chamber controls. There were significant exposure concentration-related decreases in sperm motility in males exposed to 32, 62, or 125 ppm; the estrous cycle of 125 ppm females was significantly longer than that of the chamber controls but only by half a day. Histopathologic changes were noted primarily in the nasal cavity and involved both the respiratory and olfactory epithelium of males and females principally in the 62 or 125 ppm groups. These lesions included suppurative inflammation, squamous metaplasia of the respiratory epithelium, olfactory epithelial atrophy, and necrosis of the turbinates. 2-YEAR STUDY IN RATS: Groups of 50 male and 50 female rats were exposed to diethylamine vapor at concentrations of 0, 31, 62.5, or 125 ppm, 6 hours plus T90 (15 minutes) per day, 5 days per week for 105 weeks. Survival of exposed groups of rats was similar to that of the chamber control groups. Mean body weights of males and females exposed to 125 ppm were less than those of the chamber controls after week 57. Increased incidences of eye abnormality occurred in exposed males and females. A spectrum of nonneoplastic lesions was observed in the respiratory and olfactory epithelium of the nose in exposed rats. The lesions included suppurative inflammation, ulceration of the respiratory epithelium, hyaline droplet accumulation in the glands of the respiratory epithelium, necrosis of the turbinates, squamous metaplasia of the respiratory epithelium, hyperplasia of the respiratory epithelium, atrophy of the olfactory epithelium, hyaline droplet accumulation in the respiratory and olfactory epithelium, basal cell hyperplasia of the olfactory epithelium, respiratory metaplasia of the olfactory epithelium, and goblet cell hyperplasia. The incidence of chronic inflammation of the pleura was significantly increased in 125 ppm females. The incidences of histiocytic cellular infiltration of the alveolus of the lung were significantly increased in all exposed groups of females and the incidence of chronic inflammation was significantly increased in 125 ppm females. In 125 ppm males, the incidence of suppurative inflammation of the cornea was significantly increased. 2-YEAR STUDY IN MICE: Groups of 50 male and 50 female mice were exposed to diethylamine vapor at concentrations of 0, 16, 31, or 62.5 ppm, 6 hours plus T90 (15 minutes) per day, 5 days per week for 105 weeks. Survival of exposed groups of mice was similar to that of the chamber control groups. Mean body weights of males and females were similar to those of the chamber controls. Eye abnormality was observed in greater incidence in exposed groups of males than in the chamber controls, and torso/ventral ulcer/abscess was observed in six 62.5 ppm males compared to none in the chamber controls. A similar spectrum of nonneoplastic lesions was seen in the nose of exposed mice as was seen in rats.
Diethylamine was not mutagenic in either of two independent bacterial mutagenicity assays, each conducted with and without exogenous metabolic activation enzymes. Bacterial strains tested included Salmonella typhimurium strains TA98, TA100, TA1535, and TA1537 and Escherichia coli strain WP2 uvrA/pKM101. In addition to the negative results in the two bacterial assays, no significant increases in the frequencies of micronucleated erythrocytes were seen in peripheral blood of male or female B6C3F1 mice from the 3-month study.
Under the conditions of these 2-year inhalation studies, there was no evidence of carcinogenic activity of diethylamine in male or female F344/N rats exposed to 31, 62.5, or 125 ppm. There was no evidence of carcinogenic activity of diethylamine in male or female B6C3F1 mice exposed to 16, 31, or 62.5 ppm. Exposure to diethylamine resulted in increased incidences of nonneoplastic lesions of the nose in male and female rats and mice, of the cornea in male rats, and of the pleura and lung in female rats.
二乙胺主要用作生产缓蚀剂N,N - 二乙基乙醇胺的化学中间体,少量用于生产农药、驱虫剂以及橡胶加工。美国国家环境卫生科学研究所基于二乙胺的高产量、在自然界中微量普遍存在以及缺乏该化学品的慢性毒性和致癌性数据,将其列为研究对象。对雄性和雌性F344/N大鼠以及B6C3F1小鼠进行为期2周、3个月或2年的吸入二乙胺(纯度约99.9%)实验。在细菌致突变测试菌株和小鼠外周血红细胞中进行了遗传毒理学研究。
大鼠2周研究:将每组5只雄性和5只雌性大鼠暴露于浓度为0、31、62.5、125、250或500 ppm的二乙胺蒸气中,每天6小时加T90(12分钟),每周5天,持续16天。所有大鼠均存活至研究结束。暴露于250和500 ppm的雄性和雌性大鼠以及125 ppm的雄性大鼠的平均体重显著低于实验舱对照组。临床发现包括嗜睡、鼻/眼分泌物、呼吸异常、消瘦、眼部异常和尿液变色。暴露于125 ppm及以上的雄性大鼠和500 ppm的雌性大鼠的胸腺重量显著低于实验舱对照组。在尸检时,发现4只暴露于500 ppm的雄性大鼠、3只暴露于500 ppm的雌性大鼠和1只暴露于250 ppm的雄性大鼠出现眼部局灶性病变。大多数暴露于500 ppm的雄性和雌性大鼠以及2只暴露于250 ppm的雄性大鼠出现结痂鼻子。所有暴露于125 ppm及以上的大鼠均出现化脓性炎症、鼻甲坏死(125 ppm的1只雌性大鼠除外)以及鼻呼吸上皮的鳞状化生。所有暴露于250或500 ppm的大鼠均出现呼吸上皮溃疡和嗅上皮萎缩,所有500 ppm的大鼠均出现鼻咽管溃疡。大多数暴露于500 ppm的大鼠出现角膜化脓性炎症。
小鼠2周研究:将每组5只雄性和5只雌性小鼠暴露于浓度为0、31、62.5、125、250或500 ppm的二乙胺蒸气中,每天6小时加T90(12分钟),每周5天,持续17天。2只暴露于500 ppm的雄性小鼠和3只暴露于500 ppm的雌性小鼠在研究的第一周死亡。暴露于125 ppm及以上的雄性和雌性小鼠的平均体重显著低于实验舱对照组。暴露于250或5所0 ppm的雄性和雌性小鼠在研究期间体重减轻。大多数暴露于250或500 ppm的小鼠出现嗜睡、呼吸异常和消瘦。500 ppm的小鼠出现眼部刺激和分泌物、鼻分泌物以及低粪便和尿量。暴露于250和500 ppm的雄性小鼠以及125 ppm及以上的雌性小鼠的胸腺重量显著低于实验舱对照组。所有暴露于250或500 ppm的雄性小鼠以及所有暴露于125 ppm及以上的雌性小鼠均出现鼻子化脓性炎症,大多数暴露于125 ppm的雄性小鼠也出现该症状。除1只31 ppm的雌性小鼠外,所有暴露小鼠均出现鼻甲坏死。暴露于125 ppm及以上的小鼠出现呼吸上皮鳞状化生和嗅上皮萎缩。在肺部,暴露于500 ppm的雄性小鼠主支气管轻度慢性活动性炎症的发生率显著增加。
大鼠3个月研究:将每组10只雄性和10只雌性大鼠暴露于浓度为0、8、16、32、62或125 ppm的二乙胺蒸气中,每天6小时加T90(12分钟),每周5天,持续14周。所有大鼠均存活至研究结束。所有暴露组的平均体重与实验舱对照组相似。暴露于32、62和125 ppm的雄性大鼠精子活力出现与暴露浓度相关的显著下降;实验舱对照组和暴露组雌性大鼠的发情周期长度无显著差异。与暴露相关的鼻部病变主要见于暴露于62或125 ppm的大鼠。这些病变包括鼻甲坏死、化脓性炎症、呼吸上皮增生、呼吸上皮鳞状化生和嗅上皮萎缩。
小鼠3个月研究:将每组10只雄性和10只雌性小鼠暴露于浓度为0、8、16、32、62或125 ppm的二乙胺蒸气中,每天6小时加T90(12分钟),每周5天,持续14周。所有小鼠均存活至研究结束。暴露于125 ppm的雄性和雌性小鼠的平均体重显著低于实验舱对照组。暴露于32、62或125 ppm的雄性小鼠精子活力出现与暴露浓度相关的显著下降;暴露于125 ppm 的雌性小鼠发情周期显著长于实验舱对照组,但仅长半天。组织病理学变化主要见于鼻腔,主要涉及62或125 ppm组雄性和雌性小鼠的呼吸和嗅上皮。这些病变包括化脓性炎症、呼吸上皮鳞状化生、嗅上皮萎缩和鼻甲坏死。
大鼠2年研究:将每组50只雄性和50只雌性大鼠暴露于浓度为0、31、62.5或125 ppm的二乙胺蒸气中,每天6小时加T90(15分钟),每周5天,持续105周。暴露组大鼠的存活率与实验舱对照组相似。暴露于125 ppm的雄性和雌性大鼠在第57周后平均体重低于实验舱对照组。暴露的雄性和雌性大鼠眼部异常发生率增加。在暴露大鼠的鼻子呼吸和嗅上皮中观察到一系列非肿瘤性病变。这些病变包括化脓性炎症、呼吸上皮溃疡、呼吸上皮腺体中透明滴积累、鼻甲坏死呼吸上皮鳞状化生、呼吸上皮增生、嗅上皮萎缩、呼吸和嗅上皮中透明滴积累、嗅上皮基底细胞增生、嗅上皮呼吸化生和杯状细胞增生。暴露于125 ppm的雌性大鼠胸膜慢性炎症发生率显著增加。所有暴露组雌性大鼠肺泡组织细胞浸润发生率显著增加,暴露于125 ppm的雌性大鼠慢性炎症发生率显著增加。暴露于125 ppm的雄性大鼠角膜化脓性炎症发生率显著增加。
小鼠2年研究:将每组50只雄性和50只雌性小鼠暴露于浓度为0、16、31或62.5 ppm的二乙胺蒸气中,每天6小时加T90(15分钟),每周5天,持续105周。暴露组小鼠的存活率与实验舱对照组相似。雄性和雌性小鼠的平均体重与实验舱对照组相似。暴露组雄性小鼠眼部异常发生率高于实验舱对照组,6只暴露于62.5 ppm的雄性小鼠出现躯干/腹部溃疡/脓肿,而实验舱对照组未出现。暴露小鼠鼻子中观察到与大鼠相似的一系列非肿瘤性病变。
在两种独立的细菌致突变试验中,无论有无外源性代谢激活酶,二乙胺均无致突变性。测试的细菌菌株包括鼠伤寒沙门氏菌菌株TA98、TA100、TA1535和TA1537以及大肠杆菌菌株WP2 uvrA/pKM101。除了这两种细菌试验的阴性结果外,在3个月研究的雄性或雌性B6C3F1小鼠外周血中,微核红细胞频率未见显著增加。
在这些为期2年的吸入研究条件下,未发现暴露于31、62.5或125 ppm二乙胺的雄性或雌性F344/N大鼠有致癌活性证据。未发现暴露于16、31或62.5 ppm二乙胺的雄性或雌性B6C3F1小鼠有致癌活性证据。暴露于二乙胺导致雄性和雌性大鼠及小鼠鼻子非肿瘤性病变发生率增加,雄性大鼠角膜病变发生率增加,雌性大鼠胸膜和肺部病变发生率增加。