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美国国家毒理学计划关于经吸入给予F344/N大鼠和B6C3F1小鼠2-氯硝基苯(化学物质登记号88-73-3)和4-氯硝基苯(化学物质登记号100-00-5)的毒性研究技术报告

NTP technical report on the toxicity studies of 2-Chloronitrobenzene (CAS No. 88-73-3) and 4-Chloronitrobenzene (CAS No. 100-00-5) Administered by Inhalation to F344/N Rats and B6C3F1 Mice.

作者信息

Bucher John

出版信息

Toxic Rep Ser. 1993 Jul;33:1-F25.

PMID:12209191
Abstract

2-Chloronitrobenzene and 4-chloronitrobenzene are oily yellow solids that are used primarily as chemical intermediates in the production of dyes, lumber preservatives, drugs, and photographic chemicals. Although these chemicals are solids at room temperature, the vapor pressures of these chemicals are sufficiently high to result in significant inhalation exposure. Toxicity studies of 2-chloronitrobenzene and 4-chloronitrobenzene were performed by exposing male and female F344/N rats and B6C3F1 mice to the chemicals by whole-body inhalation 6 hours per day, 5 days per week, for 2 weeks or 13 weeks. Animals were evaluated for histopathology, clinical chemistry (rats), hematology (rats), and reproductive system effects. In separate studies, the dermal absorption of the chemicals was compared, and the absorption, distribution, metabolism, and excretion were partially characterized following oral administration to male F344/N rats. 2-Chloronitrobenzene and 4-chloronitrobenzene were also administered orally to CD-1(R) Swiss mice for evaluation of reproductive and developmental toxicity. Genetic effects were evaluated in Salmonella typhimurium, in Chinese hamster ovary cells, and in Drosophila melanogaster. The highest exposure concentrations used in the 2 week and 13 week studies were limited by technical factors in vapor generation to 18 ppm (115.2 mg/m(3)) for 2-chloronitrobenzene and 24 ppm (153.6 mg/m(3)) for 4-chloronitrobenzene. Other concentrations were 0, 1.1, 2.3, 4.5, and 9 ppm (0, 7, 14.7, 28.8, and 57.6 mg/m(3)) for 2-chloronitrobenzene and 0, 1.5, 3, 6, and 12 ppm (0, 9.6, 19.2, 38.4, and 76.8 mg/m(3)) for 4-chloronitrobenzene. In 2-week studies with 2-chloronitrobenzene, all rats survived to the end of the study. One of five male mice exposed to 18 ppm died, but weight gains of exposed rats and mice were not affected. Exposed rats and mice had concentration-related increases in liver weights, and spleen weights were increased in rats and mice exposed to 18 ppm. Histopathologic findings in rats were limited to hemosiderin deposition in the liver and spleen at the highest exposure concentration. Exposed mice, primarily those in the 18 ppm groups, had coagulative necrosis, hepatocytomegaly, and granulomatous inflammation in the liver. Splenic changes including increased hematopoietic cell proliferation and hemosiderin deposition occurred at concentrations as low as 4.5 ppm. In 13-week studies with 2-chloronitrobenzene, all rats survived to the end of the study; 2 of 10 male mice exposed to 18 ppm died. Body weight gains of exposed rats and mice were similar to or somewhat higher than those of the respective controls. Methemoglobinemia occurred in rats and resulted in a normocytic, normochromic anemia that became responsive by the end of the study. Exposed rats and mice had increased liver weights, but these increases were not as great as those seen in the 2-week studies. Spleen weights were increased in exposed rats. Histopathologic changes in rats included increased basophilia of centrilobular hepatocytes, pigmentation and regeneration of the proximal convoluted tubules of the kidney, and hyperplasia of the nasal cavity respiratory epithelium. In mice, hepatocellular necrosis, cytomegaly, mineralization, and chronic inflammation occurred in the liver, primarily in mice in the 18 ppm group, and hematopoietic activity in the spleen was increased. In 2-week studies with 4-chloronitrobenzene, all rats and mice survived to the end of the studies. Body weight gains of exposed rats were similar to those of the controls; body weight gains of exposed mice were greater than those of the controls. Liver and spleen weights were increased in exposed rats and mice. In rats, histopathologic changes in the liver were limited to an increase in hemosiderin pigment in Kupffer cells. The spleens of exposed rats were congested and had increased hematopoietic activity and hemosiderin deposition. Kidneys of exposed male rats had lesions consistent with hyaline droplet nephropathy. The proximal convoluted tubules of exposed female rats c contained hemosiderin. Microscopic changes in exposed mice primarily involved increased hematopoietic activity in the spleen and hemosiderin pigmentation in the spleen, liver, and proximal convoluted tubules in the kidney. In 13-week studies with 4-chloronitrobenzene, there were no deaths that were clearly related to exposure to 4-chloronitrobenzene. Body weight gains of exposed rats and mice were either equal to or greater than those of the controls. A more severe methemoglobinemia developed in rats exposed to 4-chloronitrobenzene than occurred in rats exposed to 2-chloronitrobenzene, and this methemoglobinemia resulted in a responsive macrocytic, hyperchromic anemia. Spleen weights were markedly greater in exposed rats and mice than in controls. In exposed rats, lesions in the spleen, liver, and kidney were similar to those described for the 2-week study. Additionally, increased hematopoietic cell proliferation in bone marrow, histiocytic hyperplasia in mediastinal lymph nodes, testicular atrophy, and chronic inflammation of the harderian gland occurred in exposed rats. In exposed mice, microscopic changes in the spleen and liver were similar to those noted in the 2-week study. Additional lesions included increased hematopoiesis and hemosiderin deposition in the bone marrow of exposed males and females and squamous cell hyperplasia of the forestomach epithelium in female mice. In reproductive system assessments, there was evidence of decreased spermatogenesis in rats exposed to either 2- or 4-chloronitrobenzene. In mice, effects were limited to a decrease in sperm motility in males exposed to 2-chloronitrobenzene and an increase in estrous cycle length in females exposed to 4-chloronitrobenzene. In continuous breeding studies, a progressive decrease in fertility was noted in CD-1® Swiss mice receiving 4-chloronitrobenzene by oral gavage; fertility was not affected in mice administered 2-chloronitrobenzene by oral gavage. Percutaneous absorption of [14C]-2-chloronitrobenzene and [14C]-4-chloronitrobenzene was demonstrated in rats. For doses ranging from 0.65 to 65 mg/kg of either chemical, 33% to 40% of 2-chloronitrobenzene and 51% to 62% of 4-chloronitrobenzene were absorbed under nonocclusive conditions. Oral absorption was somewhat higher than dermal absorption for both chemicals, and metabolism was complicated, with over 20 unidentified metabolites isolated from urine of rats given either 2- or 4-chloronitrobenzene. 2-Chloronitrobenzene and 4-chloronitrobenzene were mutagenic in Salmonella typhimurium with S9 activation. In addition, both compounds induced sister chromatid exchanges and chromosomal aberrations in Chinese hamster ovary cells; requirements for S9 activation varied among testing laboratories. Neither compound induced sex-linked recessive lethal mutations in germ cells of male Drosophila melanogaster treated as adults or as larvae. In summary, inhalation exposure of rats and mice to 2- or 4-chloronitrobenzene resulted in methemoglobin formation and oxidative damage to red blood cells, leading to a regenerative anemia and a recognized spectrum of tissue damage and changes secondary to erythrocyte injury. In addition, numerous other lesions that were considered primary toxic effects occurred following exposure. These included renal hyaline droplet accumulation and testicular atrophy in male rats exposed to 4-chloronitrobenzene and hyperplasia of the respiratory epithelium in rats exposed to 2-chloronitrobenzene. A no-observed-adverse-effect-level (NOAEL) for rats was not achieved, as increases in methemoglobin and histopathologic changes occurred at exposure concentrations as low as 1.1 ppm for 2-chloronitrobenzene and 1.5 ppm for 4-chloronitrobenzene in the 13-week studies. The NOAEL for histopathologic injury in mice was 4.5 ppm for 2-chloronitrobenzene and 6 ppm for 4-chloronitrobenzene. 2-Chloronitrobenzene Synonyms: o-Cloronitrobenzene; 2-chloro-1-nitrobenzene; ONCB. 4-chloronitrobenzene Synonyms: p-Chloronitrobenzene; 4-chloro-1-nitrobenzene; PNCB.

摘要

2-氯硝基苯和4-氯硝基苯为油状黄色固体,主要用作生产染料、木材防腐剂、药物及摄影化学品的化学中间体。尽管这些化学品在室温下为固体,但它们的蒸气压足够高,可导致显著的吸入暴露。通过让雄性和雌性F344/N大鼠及B6C3F1小鼠每天6小时、每周5天、持续2周或13周全身吸入这些化学品,对2-氯硝基苯和4-氯硝基苯进行了毒性研究。对动物进行了组织病理学、临床化学(大鼠)、血液学(大鼠)及生殖系统影响的评估。在单独的研究中,比较了这些化学品的皮肤吸收情况,并对雄性F344/N大鼠口服给药后的吸收、分布、代谢及排泄进行了部分特征描述。还对CD-1(R)瑞士小鼠口服给予2-氯硝基苯和4-氯硝基苯,以评估其生殖和发育毒性。在鼠伤寒沙门氏菌、中国仓鼠卵巢细胞及黑腹果蝇中评估了遗传效应。2周和13周研究中使用的最高暴露浓度,由于蒸汽产生的技术因素,2-氯硝基苯限制为18 ppm(115.2 mg/m³),4-氯硝基苯限制为24 ppm(153.6 mg/m³)。其他浓度,2-氯硝基苯为0、1.1、2.3、4.5和9 ppm(0、7、14.7、28.8和57.6 mg/m³),4-氯硝基苯为0、1.5、3、6和12 ppm(0、9.6、19.2、38.4和76.8 mg/m³)。在2-氯硝基苯的2周研究中,所有大鼠均存活至研究结束。暴露于18 ppm的5只雄性小鼠中有1只死亡,但暴露大鼠和小鼠的体重增加未受影响。暴露大鼠和小鼠的肝脏重量随浓度增加而增加,暴露于18 ppm的大鼠和小鼠脾脏重量增加。大鼠的组织病理学发现仅限于最高暴露浓度下肝脏和脾脏中的含铁血黄素沉积。暴露小鼠,主要是18 ppm组的小鼠,肝脏出现凝固性坏死、肝细胞肿大及肉芽肿性炎症。脾脏变化包括造血细胞增殖增加和含铁血黄素沉积,在低至4.5 ppm的浓度下即可出现。在2-氯硝基苯的13周研究中,所有大鼠均存活至研究结束;暴露于18 ppm的10只雄性小鼠中有2只死亡。暴露大鼠和小鼠的体重增加与各自对照组相似或略高。大鼠出现高铁血红蛋白血症,并导致正细胞、正色素性贫血,在研究结束时恢复。暴露大鼠和小鼠的肝脏重量增加,但增加幅度不如2周研究中所见。暴露大鼠的脾脏重量增加。大鼠的组织病理学变化包括中央小叶肝细胞嗜碱性增加、肾脏近端曲管色素沉着和再生以及鼻腔呼吸上皮增生。在小鼠中,肝脏出现肝细胞坏死、肿大、矿化及慢性炎症,主要发生在18 ppm组的小鼠中,脾脏造血活性增加。在4-氯硝基苯 的2周研究中,所有大鼠和小鼠均存活至研究结束。暴露大鼠的体重增加与对照组相似;暴露小鼠的体重增加大于对照组。暴露大鼠和小鼠的肝脏和脾脏重量增加。在大鼠中,肝脏的组织病理学变化仅限于枯否细胞中含铁血黄素色素增加。暴露大鼠的脾脏充血,造血活性增加且有含铁血黄素沉积。暴露雄性大鼠的肾脏出现与透明滴状肾病一致的病变。暴露雌性大鼠的近端曲管含有含铁血黄素。暴露小鼠的微观变化主要涉及脾脏造血活性增加以及脾脏、肝脏和肾脏近端曲管中的含铁血黄素色素沉着。在4-氯硝基苯的13周研究中,没有明显与暴露于4-氯硝基苯相关的死亡。暴露大鼠和小鼠的体重增加等于或大于对照组。暴露于4-氯硝基苯的大鼠比暴露于2-氯硝基苯的大鼠出现更严重的高铁血红蛋白血症,这种高铁血红蛋白血症导致反应性大细胞、高色素性贫血。暴露大鼠和小鼠的脾脏重量明显大于对照组。在暴露大鼠中,脾脏、肝脏和肾脏的病变与2周研究中描述的相似。此外,暴露大鼠的骨髓造血细胞增殖增加、纵隔淋巴结组织细胞增生、睾丸萎缩以及哈德氏腺慢性炎症。在暴露小鼠中,脾脏和肝脏的微观变化与2周研究中 noted的相似。其他病变包括暴露雄性和雌性小鼠骨髓造血增加和含铁血黄素沉积以及雌性小鼠前胃上皮鳞状细胞增生。在生殖系统评估中,有证据表明暴露于2-氯硝基苯或4-氯硝基苯的大鼠精子发生减少。在小鼠中,影响仅限于暴露于2-氯硝基苯的雄性小鼠精子活力下降以及暴露于4-氯硝基苯的雌性小鼠发情周期延长。在连续繁殖研究中,经口灌胃给予4-氯硝基苯的CD-1®瑞士小鼠生育力逐渐下降;经口灌胃给予2-氯硝基苯的小鼠生育力未受影响。在大鼠中证实了[1 C]-2-氯硝基苯和[14 C]-4-氯硝基苯的经皮吸收。对于剂量范围为0.65至65 mg/kg的任何一种化学品,在非封闭条件下,2-氯硝基苯的33%至40%和4-氯硝基苯的51%至62%被吸收。两种化学品的口服吸收均略高于皮肤吸收,且代谢复杂,从给予2-氯硝基苯或4-氯硝基苯的大鼠尿液中分离出20多种未鉴定的代谢物。2-氯硝基苯和4-氯硝基苯在有S9激活的情况下对鼠伤寒沙门氏菌具有致突变性。此外,两种化合物均在中国仓鼠卵巢细胞中诱导了姐妹染色单体交换和染色体畸变;不同检测实验室对S9激活的要求有所不同。两种化合物均未在成年或幼虫期处理的雄性黑腹果蝇生殖细胞中诱导性连锁隐性致死突变。总之,大鼠和小鼠吸入2-氯硝基苯或4-氯硝基苯会导致高铁血红蛋白形成和红细胞氧化损伤,导致再生性贫血以及一系列公认的组织损伤和继发于红细胞损伤的变化。此外,暴露后还出现了许多被认为是主要毒性作用的其他病变。这些包括暴露于4-氯硝基苯的雄性大鼠肾脏透明滴状积聚和睾丸萎缩以及暴露于2-氯硝基苯的大鼠呼吸上皮增生。在13周研究中,对于大鼠未达到未观察到不良反应水平(NOAEL),因为在暴露浓度低至2-氯硝基苯1.1 ppm和4-氯硝基苯1.5 ppm时就出现了高铁血红蛋白增加和组织病理学变化。小鼠组织病理学损伤的NOAEL,2-氯硝基苯为4.5 ppm,4-氯硝基苯为6 ppm。2-氯硝基苯 同义词:邻氯硝基苯;2-氯-1-硝基苯;ONCB。4-氯硝基苯 同义词:对氯硝基苯;4-氯-1-硝基苯;PNCB。

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