Knaak J B, Leung H W, Stott W T, Busch J, Bilsky J
Occidental Chemical Corp. Niagara Falls, NY 14302, USA.
Rev Environ Contam Toxicol. 1997;149:1-86. doi: 10.1007/978-1-4612-2272-9_1.
The chemistry, biochemistry, toxicity, and industrial use of monoethanolamine (MEA), diethanolamine (DEA), and triethanolamine (TEA) are reviewed. The dual function groups, amino and hydroxyl, make them useful in cutting fluids and as intermediates in the production of surfactants, soaps, salts, corrosion control inhibitors, and in pharmaceutical and miscellaneous applications. In 1995, the annual U.S. production capacity for ethanolamines was 447,727 metric tons. The principal route of exposure is through skin, with some exposure occurring by inhalation of vapor and aerosols. MEA, DEA, and TEA in water penetrate rat skin at the rate of 2.9 x 10(-3), 4.36 x 10(-3) and 18 x 10(-3) cm/hr, respectively. MEA, DEA, and TEA are water-soluble ammonia derivatives, with pHs of 9-11 in water and pHa values of 9.3, 8.8, and 7.7, respectively. They are irritating to the skin, eyes, and respiratory tract, with MEA being the worst irritant, followed by DEA and TEA. The acute oral LD50s are 2.74 g/kg for MEA, 1.82 g/kg for DEA, and 2.34 g/kg for TEA (of bw), with most deaths occurring within 4 d of administration. MEA is present in nature as a nitrogenous base in phospholipids. These lipids, composed of glycerol, two fatty acid esters, phosphoric acid, and MEA, are the building blocks of biomembranes in animals. MEA is methylated to form choline, another important nitrogenous base in phospholipids and an essential vitamin. The rat dietary choline requirement is 10 mg kg-1 d-1; 30-d oral administration of MEA (160-2670 mg kg-1 d-1) to rats produced "altered" liver and kidney weights in animals ingesting 640 mg kg-1 d-1 or greater. Death occurred at dosages of 1280 mg kg-1 d-1. No treatment-related effects were noted in dogs administered as much as 22 mg kg-1 d-1 for 2 yr. DEA is not metabolized or readily eliminated from the liver or kidneys. At high tissue concentrations, DEA substitutes for MEA in phospholipids and is methylated to form phospholipids composed of N-methyl and N, N-dimethyl DEA. Dietary intake of DEA by rats for 13 wk at levels greater than 90 mg kg-1 d-1 resulted in degenerative changes in renal tubular epithelial cells and fatty degeneration of the liver. Similar effects were noted in drinking water studies. The findings are believed to be due to alterations in the structure and function of biomembranes brought about by the incorporation of DEA and methylated DEA in headgroups. TEA is not metabolized in the liver or incorporated into phospholipids. TEA, however, is readily eliminated in urine. Repeated oral administration to rats (7 d/wk, 24 wk) at dose levels up to and including 1600 mg kg-1 d-1 produced histopathological changes restricted to kidney and liver. Lesions in the liver consisted of cloudy swelling and occasional fatty changes, while cloudy swelling of the convoluted tubules and loop of Henle were observed in kidneys. Chronic administration (2 yr) of TEA in drinking water (0, 1%, or 2% w/v; 525 and 1100 mg kg-1 d-1 in males and 910 and 1970 mg kg-1 d-1 in females) depressed body and kidney weights in F-344 rats. Histopathological findings consisted of an "acceleration of so-called chronic nephropathy" commonly found in the kidneys of aging F-344 rats. In B6C3F1 mice, chronic administration of TEA in drinking water (0, 1%, or 2%) produced no significant change in terminal body weights between treated and control animals or gross pathological changes. TEA was not considered to be carcinogenic. Systemic effects in rats chronically administered TEA dermally (0, 32, 64, or 125 mg kg-1 d-1 in males; 0, 63, 125, or 250 mg kg-1 d-1 in females) 5 d/wk for 2 yr were primarily limited to hyperplasia of renal tubular epithelium and small microscopic adenomas. In a companion mouse dermal study, the most significant change was associated with nonneoplastic changes in livers of male mice consistent with chronic bacterial hepatitis.
本文综述了单乙醇胺(MEA)、二乙醇胺(DEA)和三乙醇胺(TEA)的化学性质、生物化学性质、毒性及工业用途。氨基和羟基这两个官能团使它们在切削液中很有用,并且可作为表面活性剂、肥皂、盐、缓蚀剂生产的中间体,还可用于制药及其他应用。1995年,美国乙醇胺的年生产能力为447,727公吨。主要接触途径是通过皮肤,也有一些通过吸入蒸汽和气溶胶而接触。MEA、DEA和TEA在水中穿透大鼠皮肤的速率分别为2.9×10⁻³、4.36×10⁻³和18×10⁻³厘米/小时。MEA、DEA和TEA是水溶性氨衍生物,在水中的pH值为9 - 11,pHa值分别为9.3、8.8和7.7。它们对皮肤、眼睛和呼吸道有刺激性,其中MEA刺激性最强,其次是DEA和TEA。急性经口半数致死剂量(LD50),MEA为2.74克/千克体重,DEA为1.82克/千克体重,TEA为2.34克/千克体重,大多数死亡发生在给药后4天内。MEA在自然界中作为磷脂中的含氮碱存在。这些由甘油、两个脂肪酸酯、磷酸和MEA组成的脂质是动物生物膜的组成部分。MEA甲基化形成胆碱,胆碱是磷脂中另一种重要的含氮碱和一种必需维生素。大鼠饮食中胆碱的需求量为10毫克/千克体重·天;给大鼠口服MEA(160 - 2670毫克/千克体重·天)30天,摄入640毫克/千克体重·天及以上的动物肝脏和肾脏重量“改变”。剂量为1280毫克/千克体重·天时动物死亡。给狗连续2年给予高达22毫克/千克体重·天的剂量,未观察到与治疗相关的影响。DEA在肝脏中不被代谢或不易从肝脏或肾脏中消除。在高组织浓度下,DEA在磷脂中替代MEA,并甲基化形成由N - 甲基和N,N - 二甲基DEA组成的磷脂。大鼠连续13周摄入高于90毫克/千克体重·天的DEA,导致肾小管上皮细胞退行性变化和肝脏脂肪变性。在饮用水研究中也观察到类似影响。这些发现被认为是由于DEA和甲基化DEA掺入头基团导致生物膜结构和功能改变所致。TEA在肝脏中不被代谢,也不掺入磷脂。然而,TEA很容易从尿液中排出。以高达1600毫克/千克体重·天(包括1600毫克/千克体重·天)的剂量水平给大鼠重复经口给药(每周7天,共24周),组织病理学变化仅限于肾脏和肝脏。肝脏病变包括浊肿和偶尔的脂肪变化,而在肾脏中观察到曲小管和髓袢的浊肿。在饮用水中给F - 344大鼠长期(2年)给予TEA(0、1%或2% w/v;雄性为525和1100毫克/千克体重·天,雌性为910和1970毫克/千克体重·天),导致体重和肾脏重量下降。组织病理学发现包括在衰老的F - 344大鼠肾脏中常见的“所谓慢性肾病加速”。在B6C3F1小鼠中,在饮用水中给小鼠长期给予TEA(0、1%或2%),处理组和对照组动物的终末体重及大体病理学变化无显著差异。TEA不被认为具有致癌性。给大鼠长期经皮给予TEA(雄性为0、32、64或125毫克/千克体重·天;雌性为0、63、125或250毫克/千克体重·天),每周5天,共2年,全身影响主要限于肾小管上皮增生和小的显微镜下腺瘤。在一项配套的小鼠皮肤研究中,最显著的变化与雄性小鼠肝脏的非肿瘤性变化有关,符合慢性细菌性肝炎。