国家毒理学规划关于饮用水和外用二乙醇胺对F344/N大鼠和B6C3F1小鼠毒性研究的技术报告(CAS No. 111-42-2)。

Toxicity report series Pub Date : 1992-10-01
Ronald Melnick
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In the 13-week study, deaths of mice occurred in the 3 highest dose groups; 2 male rats in the top dose group also died. Surviving animals in the higher concentration groups in both studies exhibited depressed weight gains. Rats receiving diethanolamine developed a poorly regenerative, microcytic anemia in both studies. In the 2-week study, dosed male and female rats had increased kidney weights, renal tubular cell necrosis, and decreased renal function; rats in the 13-week study also showed increased incidences or severity of nephropathy, tubular necrosis, and mineralization. Degeneration of the seminiferous tubules of the testis was noted in dosed males in both the 2- and 13-week studies, and sperm motility and count were decreased in the 13-week study. Demyelination in the brain (medulla oblongata) and spinal cord was observed in male and female rats in the 13-week study. 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引用次数: 0

摘要

二乙醇胺是一种高产化学品,用于化妆品、切削液、农用化学品的分散剂和酸性气体的吸收剂。对F344/N大鼠和B6C3F1小鼠进行了为期2周(5个性别/种/剂量)和13周(10个性别/种/剂量)的二乙醇胺毒理学研究,以表征和比较口服和皮肤暴露的影响。除组织病理学外,评估还包括临床病理学、尿液分析、精子形态或阴道细胞学。体外遗传毒性研究包括鼠伤寒沙门菌和小鼠淋巴瘤L5178Y细胞的致突变性评估,中国仓鼠卵巢细胞染色体畸变和姐妹染色单体交换分析,以及小鼠在13周皮肤暴露研究中形成的微核测定。在为期2周或13周的研究中,各组大鼠和小鼠接受含有浓度高达10000 ppm的二乙醇胺的饮用水。在为期两周的研究中,男女大鼠和小鼠在饮用水中分别摄入了0、630、1250、5000和10000 ppm的二乙醇胺。在为期13周的研究中,大鼠接受0、320、630、1250、2500和5000 ppm(雄性)或0、160、320、630、1250和2500 ppm(雌性)的饮用水;雄性和雌性小鼠分别接受0、630、1250、2500、5000和10000 ppm。在为期两周的研究中,两个最高剂量组的所有雌性大鼠和10000 ppm组的2只雄性大鼠在研究结束前死亡。在13周的研究中,3个最高剂量组均有小鼠死亡;高剂量组2只雄性大鼠死亡。在两项研究中,高浓度组中存活的动物体重增加受到抑制。在两项研究中,接受二乙醇胺治疗的大鼠都出现了再生能力差的小细胞性贫血。在2周的研究中,给药的雄性和雌性大鼠肾脏重量增加,肾小管细胞坏死,肾功能下降;在为期13周的研究中,大鼠还表现出肾病、肾小管坏死和矿化的发生率或严重程度增加。在第2周和第13周的研究中,在给药的男性中都发现了睾丸精管的退化,在第13周的研究中,精子活力和数量减少。在13周的研究中,雌雄大鼠均观察到脑(延髓)和脊髓脱髓鞘。在小鼠中,在2周的研究中观察到雄性和雌性肝脏重量的剂量依赖性增加;高剂量组肝细胞发生细胞学改变和坏死。在小鼠13周的饮水研究中,雄性小鼠出现肾病和肾小管坏死,雌雄小鼠心肌细胞变性和肝细胞坏死。雌雄小鼠下颌下唾液腺均有细胞学改变。肝细胞细胞学改变也在所有给药组小鼠中被注意到。在为期2周的皮肤研究中,各组大鼠和小鼠每天服用95%乙醇中的二乙醇胺,小鼠剂量为160至2500 mg/kg,大鼠剂量为125至2000 mg/kg,每周5天。在为期13周的研究中,大鼠的皮肤剂量为32至500 mg/kg,小鼠为80至1250 mg/kg。在2周的研究中,最高剂量组出现雄性大鼠和雌雄小鼠的早期死亡,2个最高剂量组(1000和2000 mg/kg)出现雌性大鼠的早期死亡。高剂量组的大鼠和小鼠体重增加减少。在为期13周的研究中,在最高剂量组大鼠(500 mg/kg)和小鼠(1250 mg/kg)中观察到早期死亡。给予较高剂量的大鼠和小鼠体重增加减少。皮肤研究中的大鼠表现出与饮用水研究中观察到的大鼠相似的剂量依赖性血液学和肾功能变化。此外,在为期2周的研究中,大鼠在施用部位出现溃疡性皮肤病变,并伴有炎症细胞浸润、角化过度和表皮真皮棘层增生。在一些动物中观察到角化过度,无溃疡。在雄性和雌性小鼠中观察到应用部位的溃疡。在所有低剂量组小鼠中均观察到棘皮增生,无溃疡或炎症细胞浸润。在为期13周的研究中,涂抹部位的皮肤病变包括溃疡和炎症、角化过度和棘层增生。雄性和雌性大鼠的肝脏重量增加,但没有相关的组织病理学改变。在大鼠中观察到的其他治疗相关效应包括脑和脊髓脱髓鞘、肾病、肾小管坏死和/或肾小管矿化;小鼠表现出肝脏和/或肝细胞坏死、肾小管上皮坏死和心肌细胞变性的细胞学改变。 在体外遗传毒性研究中,二乙醇胺对鼠伤寒沙门菌和小鼠L5178Y TK&plusmn没有诱变作用;细胞。二乙醇胺未引起中国仓鼠卵巢细胞的姐妹染色单体交换或染色体畸变,也未引起外用13周小鼠外周血红细胞微核。所有的体外研究都是在S9激活和不激活的情况下进行的。在这些研究中确定的二乙醇胺毒性靶器官包括大鼠的骨髓、肾脏、脑、脊髓、睾丸和皮肤,以及小鼠的肝脏、肾脏、心脏、唾液腺和皮肤。在饮用水研究中,大鼠血液学改变或肾病(160 ppm)或小鼠肝脏细胞学改变(630 ppm)未达到未观察到的不良反应水平(NOAEL)。在皮肤研究中,大鼠血液学改变、肾病或皮肤角化过度(32 mg/kg)或小鼠肝脏细胞学改变或皮肤棘层增生(80 mg/kg)均未达到NOAEL。同义词:2 2 &vprime; -iminodiethanol;2、2 &vprime; -iminobisethanol;diethylolamine;bis(羟乙基)胺;2、2 'dihydroxydiethylamine;2、2 &vprime; -aminodiethanol。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
NTP technical report on the toxicity studies of Diethanolamine (CAS No. 111-42-2) Administered Topically and in Drinking Water to F344/N Rats and B6C3F1 Mice.

Diethanolamine is a high-production chemical used in cosmetics, in cutting fluids, as a dispersing agent for agricultural chemicals, and as an absorbent for acidic gases. Toxicology studies of diethanolamine were conducted in F344/N rats and B6C3F1 mice of both sexes for 2 weeks (5/sex/species/dose) and 13 weeks (10/sex/species/dose) to characterize and compare the effects of oral and dermal exposure. In addition to histopathology, evaluations included clinical pathology, urinalyses, and sperm morphology or vaginal cytology. In vitro genetic toxicity studies included assessments of mutagenicity in Salmonella typhimurium and mouse lymphoma L5178Y cells, analysis of chromosomal aberrations and sister chromatid exchange in Chinese hamster ovary cells, and determination of micronuclei formed in mice during the 13-week dermal exposure study. Groups of rats and mice received drinking water containing diethanolamine at concentrations of up to 10000 ppm during studies of 2 or 13 weeks duration. In the 2-week studies, rats and mice of both sexes received in the were 0, 630, 1250, 5000, and 10000 ppm diethanolamine in the drinking water. In the 13-week studies, rats received 0, 320, 630, 1250, 2500, and 5000 ppm (males) or 0, 160, 320, 630, 1250, and 2500 ppm (females) in drinking water; male and female mice received 0, 630, 1250, 2500, 5000, and 10000 ppm. All female rats in the 2 highest dose groups and 2 males in the 10000 ppm group in the 2-week study died before the end of the study. In the 13-week study, deaths of mice occurred in the 3 highest dose groups; 2 male rats in the top dose group also died. Surviving animals in the higher concentration groups in both studies exhibited depressed weight gains. Rats receiving diethanolamine developed a poorly regenerative, microcytic anemia in both studies. In the 2-week study, dosed male and female rats had increased kidney weights, renal tubular cell necrosis, and decreased renal function; rats in the 13-week study also showed increased incidences or severity of nephropathy, tubular necrosis, and mineralization. Degeneration of the seminiferous tubules of the testis was noted in dosed males in both the 2- and 13-week studies, and sperm motility and count were decreased in the 13-week study. Demyelination in the brain (medulla oblongata) and spinal cord was observed in male and female rats in the 13-week study. In mice, dose-dependent increases in liver weight were observed in males and females in the 2-week study; cytologic alteration and necrosis of individual hepatocytes were observed in the highest dose group. In the 13-week drinking water study in mice, nephropathy and tubular necrosis were observed in males, and degeneration of cardiac myocytes, and hepatocellular necrosis were seen in males and females. Cytologic alteration in the submandibular salivary gland was noted in male and female mice. Hepatocyte cytologic alteration also was noted in all dosed groups of mice. In the 2-week dermal studies, groups of rats and mice were administered daily doses of diethanolamine in 95% ethanol, ranging from 160 to 2500 mg/kg for mice, and from 125 to 2000 mg/kg for rats, 5 days per week. In 13-week studies, dermal doses ranged from 32 to 500 mg/kg for rats, and from 80 to 1250 mg/kg for mice. In the 2-week study, early deaths of male rats and male and female mice occurred in the highest dose groups and in female rats in the 2 highest dose groups (1000 and 2000 mg/kg). Body weight gains were reduced in rats and mice in the higher dose groups. Early deaths in the 13-week study were observed in the highest dose groups of rats (500 mg/kg) and mice (1250 mg/kg). Body weight gains were reduced in rats and mice given the higher doses. Rats in the dermal studies exhibited dose-dependent hematologic and renal function changes similar to those observed in rats in the drinking water study. In addition, in the 2-week study, rats exhibited ulcerative skin lesions at the site of application, accompanied by inflammatory cell infiltration, hyperkeratosis, and acanthosis (hyperplasia) of the epidermis.dermis. Hyperkeratosis, without ulceration, was observed in some animals. Ulceration at the site of application was observed in male and female mice. Acanthosis, without ulceration or inflammatory cell infiltration, was observed in mice in all lower dose groups. In the 13-week study, skin lesions at the site of application included ulceration and inflammation, hyperkeratosis, and acanthosis. Liver weights were increased in male and female rats, but there were no associated histopathological changes. Other treatment-related effects observed in rats included demyelination in the brain and spinal cord, and nephropathy, renal tubular necrosis, and/or tubular mineralization; mice exhibited cytological alterations in the liver and/or hepatocellular necrosis, renal tubular epithelial necrosis, and cardiac myocyte degeneration. In in vitro genetic toxicity studies, diethanolamine was not mutagenic in Salmonella typhimurium or mouse L5178Y TK± cells. Diethanolamine did not induce sister-chromatid exchanges or chromosomal aberrations in Chinese hamster ovary cells, nor did it induce micronuclei in peripheral blood erythrocytes in mice exposed by topical application for 13 weeks. All in vitro studies were conducted with and without S9 activation. Target organs of diethanolamine toxicity identified in these studies included bone marrow, kidney, brain, spinal cord, testis, and skin in rats, and liver, kidney, heart, salivary gland, and skin in mice. A no-observed-adverse-effect-level (NOAEL) was not achieved for hematological changes or nephropathy in rats (<160 ppm), or for cytologic alteration of the liver in mice (<630 ppm) in the drinking water studies. In the dermal studies, a NOAEL was not achieved for hematological changes, nephropathy, or hyperkeratosis of the skin in rats (<32 mg/kg), or for cytologic alteration of the liver or acanthosis of the skin in mice (<80 mg/kg). Synonyms: 2,2&vprime;-iminodiethanol; 2,2&vprime;-iminobisethanol; diethylolamine; bis(hydroxy-ethyl)amine; 2,2'dihydroxydiethylamine; 2,2&vprime;-aminodiethanol.

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