NTP technical report on the toxicity studies of 1,6-Hexanediamine Dihydrochloride (CAS No. 6055-52-3) Administered by Drinking Water and Inhalation to F344/N Rats and B6C3F1 Mice.

Toxicity report series Pub Date : 1993-03-01
Charles Hebert
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In addition, the genetic toxicity of HDA was assessed in Salmonella typhimurium and in Chinese hamster ovary cells in vitro; HDDC was evaluated in the mouse micronucleus assay in vivo. In the 2-week drinking water studies, groups of 5 rats of each sex received HDDC at doses of 0.75 to 6.7 mg/mL, and groups of 5 mice of each sex received doses of 0.2 to 3.0 mg/mL for 14 or 15 days. All animals survived to the end of the studies. No gross or microscopic pathologic changes and no clinical abnormalities related to HDDC consumption were seen in any dose group. The only statistically significant change was a slight decrease in absolute and/or relative liver weights of female rats in the 1.7, 5.0, and 6.7-mg/mL treatment groups, in male rats in the 3.0 mg/mL treatment group, and in female mice in the 0.8 mg/mL treatment group. Because there was no significant toxicity in these studies, 13-week drinking water studies were not conducted. In the 2-week inhalation studies, 5 rats and 5 mice of each sex were exposed to 0, 10, 30, 89, 267, or 800 mg HDDC/m(3) for 6-hours per day for 12 days. In the highest exposure group (800 mg/m(3)), all male and female rats, all female mice, and 2 male mice died before the end of the studies. In the remaining groups, there was a dose-dependent depression in body weight gain in male and female mice, but not in rats. Clinical signs were primarily related to upper respiratory tract irritation and included dyspnea and nasal discharge in rats and mice. Absolute and relative liver weights were reduced in some male mice, but this did not occur in a dose- dependent manner. In rats, histopathologic lesions that were considered related to chemical exposure included inflammation and necrosis of laryngeal epithelium as well as focal inflammation and ulceration of the respiratory and olfactory nasal mucosa. In mice, focal areas of inflammation and necrosis were present in the respiratory mucosa of the larynx and trachea in the 2 highest exposure groups. Nasal lesions, including focal inflammation and ulceration, and degeneration and necrosis of the olfactory and respiratory epithelium were also seen in mice. In addition, mild testicular degeneration was present in 2 mice from the highest exposure group (800 mg/m(3)). In the 13-week inhalation studies, 10 rats and 10 mice of each sex were exposed to 0, 1.6, 5, 16, 50, or 160 mg HDDC/m(3) for 6 hours per day, 5 days per week for 13 weeks. In addition special groups of 20 male and 40 female rats and mice (mating trial animals) at each exposure level were included to assess the effect of HDDC on reproduction. All rats and mice in the base-study groups survived to the end of the studies, and there were no exposure-related changes in body weight. In the mating trials, 3 female mice exposed to 16 mg/m(3) and 1 female and 1 male mouse exposed to 50 mg/m(3) died before scheduled termination. These deaths, however, were not considered to be chemical related. In male mice in the base study, liver weights were increased relative to controls in the 2-highest exposure groups. No exposure-related changes in absolute or relative organ weights and no exposure-related clinical signs or gross lesions were seen in either species. In female rats, a dose-related decrease in white blood cell count was observed. Chemical-related microscopic lesions in male and female rats and mice were limited to the upper respiratory tract (larynx and nasal passages) in the 2 highest exposure groups and were similar in both species. These lesions included minimal to mild focal erosion/ulceration, inflammation, and hyperplasia of the laryngeal epithelium as well as degeneration of the olfactory and respiratory nasal epithelium. HDDC caused no significant changes in sperm morphology or in the length of the estrous cycle of rats or mice. In mating trials, HDDC demonstrated no adverse effects on reproduction of rats. The only statistically significant changes in reproductive parameters of mice were a slight increase in gestation length in the 50 mg/m(3) and 160 mg/m(3) exposure groups and a decrease in mean pup weight on Day 21 in the highest exposure group. These changes were not considered to be biologically significant. 1,6-Hexanediamine was not mutagenic in 4 strains of Salmonella typhimurium, and it did not induce sister chromatid exchanges or chromosomal aberrations in cultured Chinese hamster ovary cells. These in vitro tests were conducted with and without exogenous metabolic activation (S9). Negative results were also obtained in an in vivo test that measured the frequency of micronucleated erythrocytes in peripheral blood of male and female mice. In summary, the toxicity of HDDC to rats and mice resulted from irritant properties of the chemical and was consistent with the effects of other irritant chemicals administered by inhalation. This toxicity was limited to the nose and airways. In the 2-week inhalation studies, deaths occurred in both rats and mice at the highest exposure level (800 mg/m(3)). In the 13-week studies, the no-observed-adverse-effect-level (NOAEL) for respiratory damage was 5 mg/m(3) for rats and mice. HDDC had no adverse effect on reproduction of either species and was not genotoxic. Synonyms: Hexamethylenediamine dihydrochloride; 1,6-diaminohexane dihydrochloride; 1,6-hexamethylenediamine dihydrochloride; 1,6- hexylenediamine dihydrochloride; 1,6-diamino-n-hexane dihydrochloride; HMDA; HDA; HDDC.</p>","PeriodicalId":23116,"journal":{"name":"Toxicity report series","volume":"24 ","pages":"1-D8"},"PeriodicalIF":0.0000,"publicationDate":"1993-03-01","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}
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Abstract

1,6-Hexanediamine (HDA) is an aliphatic amine that is produced in large volumes in the United States. HDA is widely used as a corrosion inhibitor in lubricants and as an intermediate in the industrial synthesis of paints, resins, inks, and textiles. Toxicity studies of the dihydrochloride salt of HDA (HDDC) were conducted in male and female Fischer 344/N rats and B6C3F1 mice by the drinking water (2-week studies only) and whole-body inhalation routes (2-week and 13-week studies). Animals were evaluated for histopathology, clinical chemistry, hematology, and reproductive toxicity. In addition, the genetic toxicity of HDA was assessed in Salmonella typhimurium and in Chinese hamster ovary cells in vitro; HDDC was evaluated in the mouse micronucleus assay in vivo. In the 2-week drinking water studies, groups of 5 rats of each sex received HDDC at doses of 0.75 to 6.7 mg/mL, and groups of 5 mice of each sex received doses of 0.2 to 3.0 mg/mL for 14 or 15 days. All animals survived to the end of the studies. No gross or microscopic pathologic changes and no clinical abnormalities related to HDDC consumption were seen in any dose group. The only statistically significant change was a slight decrease in absolute and/or relative liver weights of female rats in the 1.7, 5.0, and 6.7-mg/mL treatment groups, in male rats in the 3.0 mg/mL treatment group, and in female mice in the 0.8 mg/mL treatment group. Because there was no significant toxicity in these studies, 13-week drinking water studies were not conducted. In the 2-week inhalation studies, 5 rats and 5 mice of each sex were exposed to 0, 10, 30, 89, 267, or 800 mg HDDC/m(3) for 6-hours per day for 12 days. In the highest exposure group (800 mg/m(3)), all male and female rats, all female mice, and 2 male mice died before the end of the studies. In the remaining groups, there was a dose-dependent depression in body weight gain in male and female mice, but not in rats. Clinical signs were primarily related to upper respiratory tract irritation and included dyspnea and nasal discharge in rats and mice. Absolute and relative liver weights were reduced in some male mice, but this did not occur in a dose- dependent manner. In rats, histopathologic lesions that were considered related to chemical exposure included inflammation and necrosis of laryngeal epithelium as well as focal inflammation and ulceration of the respiratory and olfactory nasal mucosa. In mice, focal areas of inflammation and necrosis were present in the respiratory mucosa of the larynx and trachea in the 2 highest exposure groups. Nasal lesions, including focal inflammation and ulceration, and degeneration and necrosis of the olfactory and respiratory epithelium were also seen in mice. In addition, mild testicular degeneration was present in 2 mice from the highest exposure group (800 mg/m(3)). In the 13-week inhalation studies, 10 rats and 10 mice of each sex were exposed to 0, 1.6, 5, 16, 50, or 160 mg HDDC/m(3) for 6 hours per day, 5 days per week for 13 weeks. In addition special groups of 20 male and 40 female rats and mice (mating trial animals) at each exposure level were included to assess the effect of HDDC on reproduction. All rats and mice in the base-study groups survived to the end of the studies, and there were no exposure-related changes in body weight. In the mating trials, 3 female mice exposed to 16 mg/m(3) and 1 female and 1 male mouse exposed to 50 mg/m(3) died before scheduled termination. These deaths, however, were not considered to be chemical related. In male mice in the base study, liver weights were increased relative to controls in the 2-highest exposure groups. No exposure-related changes in absolute or relative organ weights and no exposure-related clinical signs or gross lesions were seen in either species. In female rats, a dose-related decrease in white blood cell count was observed. Chemical-related microscopic lesions in male and female rats and mice were limited to the upper respiratory tract (larynx and nasal passages) in the 2 highest exposure groups and were similar in both species. These lesions included minimal to mild focal erosion/ulceration, inflammation, and hyperplasia of the laryngeal epithelium as well as degeneration of the olfactory and respiratory nasal epithelium. HDDC caused no significant changes in sperm morphology or in the length of the estrous cycle of rats or mice. In mating trials, HDDC demonstrated no adverse effects on reproduction of rats. The only statistically significant changes in reproductive parameters of mice were a slight increase in gestation length in the 50 mg/m(3) and 160 mg/m(3) exposure groups and a decrease in mean pup weight on Day 21 in the highest exposure group. These changes were not considered to be biologically significant. 1,6-Hexanediamine was not mutagenic in 4 strains of Salmonella typhimurium, and it did not induce sister chromatid exchanges or chromosomal aberrations in cultured Chinese hamster ovary cells. These in vitro tests were conducted with and without exogenous metabolic activation (S9). Negative results were also obtained in an in vivo test that measured the frequency of micronucleated erythrocytes in peripheral blood of male and female mice. In summary, the toxicity of HDDC to rats and mice resulted from irritant properties of the chemical and was consistent with the effects of other irritant chemicals administered by inhalation. This toxicity was limited to the nose and airways. In the 2-week inhalation studies, deaths occurred in both rats and mice at the highest exposure level (800 mg/m(3)). In the 13-week studies, the no-observed-adverse-effect-level (NOAEL) for respiratory damage was 5 mg/m(3) for rats and mice. HDDC had no adverse effect on reproduction of either species and was not genotoxic. Synonyms: Hexamethylenediamine dihydrochloride; 1,6-diaminohexane dihydrochloride; 1,6-hexamethylenediamine dihydrochloride; 1,6- hexylenediamine dihydrochloride; 1,6-diamino-n-hexane dihydrochloride; HMDA; HDA; HDDC.

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国家毒理学规划关于1,6-己二胺盐酸(CAS No. 6055-52-3)饮水和吸入给药对F344/N大鼠和B6C3F1小鼠毒性研究的技术报告。
1,6-己二胺(HDA)是一种脂肪胺,在美国大量生产。HDA被广泛用作润滑剂中的缓蚀剂,并作为油漆、树脂、油墨和纺织品工业合成的中间体。采用饮水(仅2周研究)和全身吸入(2周和13周研究)两种方法对雄性和雌性Fischer 344/N大鼠和B6C3F1小鼠进行盐酸HDA (HDDC)的毒性研究。对动物进行组织病理学、临床化学、血液学和生殖毒性评估。并对鼠伤寒沙门菌和中国仓鼠卵巢细胞进行遗传毒性评价;用小鼠体内微核试验评价HDDC。在为期2周的饮用水研究中,每性别5只大鼠每组接受0.75 - 6.7 mg/mL剂量的HDDC,每性别5只小鼠每组接受0.2 - 3.0 mg/mL剂量的HDDC,持续14或15天。所有的动物都活到了研究结束。在任何剂量组均未见HDDC消耗相关的肉眼或显微镜病理改变和临床异常。唯一有统计学意义的变化是1.7、5.0和6.7 mg/mL处理组雌性大鼠、3.0 mg/mL处理组雄性大鼠和0.8 mg/mL处理组雌性大鼠的绝对和/或相对肝脏重量略有下降。因为在这些研究中没有明显的毒性,所以没有进行为期13周的饮用水研究。在为期2周的吸入研究中,各性别5只大鼠和5只小鼠分别暴露于0、10、30、89、267或800 mg HDDC/m(3),每天6小时,持续12天。在最高暴露组(800 mg/m)中,所有雄性和雌性大鼠、所有雌性小鼠和2只雄性小鼠在研究结束前死亡。在其余组中,雄性和雌性小鼠的体重增加都有剂量依赖性的抑制,但在大鼠中没有。临床症状主要与上呼吸道刺激有关,包括大鼠和小鼠呼吸困难和流鼻水。在一些雄性小鼠中,绝对和相对肝脏重量减轻,但这种情况不以剂量依赖的方式发生。在大鼠中,被认为与化学暴露有关的组织病理学病变包括喉部上皮的炎症和坏死,以及呼吸道和嗅觉鼻粘膜的局灶性炎症和溃疡。在小鼠中,在2个最高暴露组中,喉部和气管的呼吸粘膜出现局灶性炎症和坏死。小鼠的鼻腔病变,包括局灶性炎症和溃疡,以及嗅觉和呼吸上皮的变性和坏死。此外,最高暴露组(800 mg/m)的2只小鼠出现轻度睾丸变性(3)。在为期13周的吸入研究中,各性别10只大鼠和10只小鼠分别暴露于0、1.6、5、16、50或160 mg HDDC/m(3),每天6小时,每周5天,持续13周。此外,在每种暴露水平下,包括20只雄性和40只雌性大鼠和小鼠(交配试验动物)的特殊组,以评估HDDC对生殖的影响。基础研究组中的所有大鼠和小鼠都存活到研究结束,并且体重没有与暴露相关的变化。在交配试验中,暴露于16 mg/m(3)的3只雌性小鼠和暴露于50 mg/m(3)的1只雌性和1只雄性小鼠在预定终止前死亡。然而,这些死亡被认为与化学物质无关。在基础研究的雄性小鼠中,在两个最高暴露组中,肝脏重量相对于对照组增加。两种动物均未见绝对或相对器官重量的暴露相关变化,也未见暴露相关的临床症状或大体病变。在雌性大鼠中,观察到白细胞计数的剂量相关减少。在两个最高暴露组中,雄性和雌性大鼠和小鼠的化学相关显微病变仅限于上呼吸道(喉部和鼻道),并且在两个物种中相似。这些病变包括轻微到轻度的局灶性糜烂/溃疡、炎症、喉上皮增生以及嗅觉和呼吸性鼻上皮变性。HDDC对大鼠或小鼠的精子形态和发情周期长度没有显著影响。在交配试验中,HDDC对大鼠的繁殖没有不良影响。50 mg/m(3)和160 mg/m(3)剂量组小鼠的妊娠期长度略有增加,最高剂量组小鼠第21天的平均幼仔体重有所下降,这是小鼠生殖参数有统计学意义的变化。这些变化被认为没有生物学意义。1,6-己二胺对4株鼠伤寒沙门菌无诱变作用,对培养的中国仓鼠卵巢细胞无姐妹染色单体交换或染色体畸变。 这些体外试验在有和没有外源性代谢激活的情况下进行(S9)。在测量雄性和雌性小鼠外周血微核红细胞频率的体内试验中也获得了阴性结果。总之,HDDC对大鼠和小鼠的毒性是由于该化学物质的刺激性,并且与吸入其他刺激性化学物质的作用一致。这种毒性仅限于鼻子和呼吸道。在为期2周的吸入研究中,在最高暴露水平(800 mg/m)下,大鼠和小鼠均发生死亡。在为期13周的研究中,大鼠和小鼠的呼吸损伤的未观察到不良反应水平(NOAEL)为5 mg/m(3)。HDDC对两种物种的繁殖均无不良影响,也无遗传毒性。二盐酸己二胺;1、6-diaminohexane盐酸盐;1、6-hexamethylenediamine盐酸盐;1,6-二盐酸己二胺;1、6-diamino-n-hexane盐酸盐;HMDA;,注重科技进步HDDC。
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