2-氯硝基苯(CAS No. 88-73-3)和4-氯硝基苯(CAS No. 100-00-5)吸入对F344/N大鼠和B6C3F1小鼠的毒性研究技术报告。

Toxicity report series Pub Date : 1993-07-01
John Bucher
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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&reg; 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&percnt; to 40&percnt; of 2-chloronitrobenzene and 51&percnt; to 62&percnt; 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.</p>","PeriodicalId":23116,"journal":{"name":"Toxicity report series","volume":"33 ","pages":"1-F25"},"PeriodicalIF":0.0000,"publicationDate":"1993-07-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"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.\",\"authors\":\"John Bucher\",\"doi\":\"\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<p><p>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. 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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. 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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&reg; 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&percnt; to 40&percnt; of 2-chloronitrobenzene and 51&percnt; to 62&percnt; 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. 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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.</p>\",\"PeriodicalId\":23116,\"journal\":{\"name\":\"Toxicity report series\",\"volume\":\"33 \",\"pages\":\"1-F25\"},\"PeriodicalIF\":0.0000,\"publicationDate\":\"1993-07-01\",\"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}","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}
引用次数: 0

摘要

2-氯硝基苯和4-氯硝基苯是含油的黄色固体,主要用作生产染料、木材防腐剂、药品和照相化学品的化学中间体。虽然这些化学物质在室温下是固体,但这些化学物质的蒸气压足够高,足以导致严重的吸入暴露。研究方法为F344/N大鼠和B6C3F1小鼠,分别每天6小时、每周5天、连续2周和13周全身吸入2-氯硝基苯和4-氯硝基苯的毒性。对动物进行组织病理学、临床化学(大鼠)、血液学(大鼠)和生殖系统影响的评估。在单独的研究中,比较了这些化学物质的皮肤吸收,并对雄性F344/N大鼠口服后的吸收、分布、代谢和排泄进行了部分表征。2-氯硝基苯和4-氯硝基苯也被口服给药CD-1(R)瑞士小鼠,以评估其生殖和发育毒性。研究了鼠伤寒沙门菌、中国仓鼠卵巢细胞和黑腹果蝇的遗传效应。在为期2周和13周的研究中,由于蒸汽产生的技术因素,使用的最高暴露浓度被限制在2-氯硝基苯的18 ppm (115.2 mg/m(3))和4-氯硝基苯的24 ppm (153.6 mg/m(3))。2-氯硝基苯的其他浓度分别为0、1.1、2.3、4.5和9 ppm(0、7、14.7、28.8和57.6 mg/m(3)), 4-氯硝基苯的浓度为0、1.5、3、6和12 ppm(0、9.6、19.2、38.4和76.8 mg/m(3))。在2-氯硝基苯2周的研究中,所有大鼠都存活到研究结束。暴露于18ppm的5只雄性小鼠中有1只死亡,但暴露于18ppm的大鼠和小鼠的体重增加没有受到影响。暴露于18ppm的大鼠和小鼠肝脏重量呈浓度相关增加,脾脏重量增加。大鼠的组织病理学结果仅限于在最高暴露浓度下在肝脏和脾脏中的铁血黄素沉积。暴露的小鼠,主要是那些在18ppm组,有凝固性坏死,肝细胞肥大,肝脏肉芽肿性炎症。脾脏变化包括造血细胞增殖增加和含铁血黄素沉积,浓度低至4.5 ppm。在为期13周的2-氯硝基苯研究中,所有大鼠都存活到研究结束;暴露于18ppm的10只雄性小鼠中有2只死亡。暴露的大鼠和小鼠的体重增加与各自的对照组相似或略高于对照组。高铁血红蛋白血症发生在大鼠身上,导致正红细胞、正色贫血,在研究结束时变得有反应。暴露在辐射中的大鼠和小鼠肝脏重量增加了,但这种增加没有两周研究中看到的那么大。暴露大鼠脾脏重量增加。大鼠的组织病理学改变包括小叶中心肝细胞嗜碱性增加,肾脏近曲小管色素沉着和再生,鼻腔呼吸上皮增生。在小鼠中,肝细胞坏死、巨细胞症、矿化和慢性炎症发生在肝脏,主要发生在18 ppm组的小鼠中,脾脏的造血活性增加。在4-氯硝基苯2周的研究中,所有大鼠和小鼠都存活到研究结束。暴露的大鼠体重增加与对照组相似;受辐射小鼠的体重增加幅度大于对照组。暴露的大鼠和小鼠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库普弗细胞中含铁血黄素色素的增加。暴露大鼠脾脏充血,造血活性增高,含铁血黄素沉积增多。暴露的雄性大鼠肾脏病变与透明液滴肾病一致。暴露雌性大鼠近曲小管含有含铁血黄素。暴露小鼠的微观变化主要包括脾脏造血活性增加和脾脏、肝脏和肾脏近曲小管含铁血黄素色素沉着。在为期13周的4-氯硝基苯研究中,没有发现明显与接触4-氯硝基苯有关的死亡病例。受辐射的大鼠和小鼠的体重增加等于或大于对照组。暴露于4-氯硝基苯的大鼠出现了比暴露于2-氯硝基苯的大鼠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性高色素贫血。暴露的大鼠和小鼠的脾脏重量明显大于对照组。在暴露的大鼠中,脾脏、肝脏和肾脏的损伤与2周研究中描述的相似。 此外,暴露大鼠骨髓造血细胞增殖增加,纵隔淋巴结组织细胞增生,睾丸萎缩和硬腺慢性炎症发生。在暴露的小鼠中,脾脏和肝脏的微观变化与2周研究中注意到的相似。其他病变包括暴露的雄性和雌性小鼠骨髓造血功能和含铁血黄素沉积增加,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-氯硝基苯的雄性精子活力下降和暴露于4-氯硝基苯的雌性发情周期长度增加。在连续育种研究中,CD-1&reg;4-氯硝基苯灌胃瑞士小鼠;2-氯硝基苯灌胃对小鼠生育能力无影响。大鼠经皮吸收[14C]-2-氯硝基苯和[14C]-4-氯硝基苯。对于任何一种化学品的剂量范围为0.65至65毫克/公斤,33%;40 &percnt;2-氯硝基苯和51%;到62 &percnt;4-氯硝基苯在非封闭条件下被吸收。这两种化学物质的口服吸收略高于皮肤吸收,并且代谢复杂,从给予2-或4-氯硝基苯的大鼠尿液中分离出20多种不明代谢物。2-氯硝基苯和4-氯硝基苯对鼠伤寒沙门菌具有诱变作用。此外,两种化合物均可诱导中国仓鼠卵巢细胞的姐妹染色单体交换和染色体畸变;不同实验室对S9活化的要求不同。这两种化合物都不会在雄性黑腹果蝇成年或幼虫的生殖细胞中引起性连锁的隐性致死突变。综上所述,大鼠和小鼠吸入2-或4-氯硝基苯可导致高铁血红蛋白形成和红细胞氧化损伤,导致再生性贫血和红细胞损伤继发的一系列组织损伤和变化。此外,暴露后还发生了许多被认为是原发性毒性作用的其他病变。暴露于4-氯硝基苯的雄性大鼠出现肾透明素滴积聚和睾丸萎缩,暴露于2-氯硝基苯的大鼠出现呼吸上皮增生。在为期13周的研究中,2-氯硝基苯暴露浓度低至1.1 ppm, 4-氯硝基苯暴露浓度低至1.5 ppm时,大鼠的高铁血红蛋白和组织病理学变化增加,因此未达到未观察到的不良反应水平(NOAEL)。2-氯硝基苯对小鼠组织病理学损伤的NOAEL为4.5 ppm, 4-氯硝基苯为6 ppm。氯硝基苯同义词:邻氯硝基苯;2-chloro-1-nitrobenzene;ONCB。4-氯硝基苯对氯硝基苯;4-chloro-1-nitrobenzene;PNCB。
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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.

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.

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