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硫化镍(CAS编号:12035-72-2)对F344大鼠和B6C3F1小鼠的NTP毒理学和致癌性研究(吸入研究)

NTP Toxicology and Carcinogenesis Studies of Nickel Subsulfide (CAS No. 12035-72-2) in F344 Rats and B6C3F1 Mice (Inhalation Studies).

出版信息

Natl Toxicol Program Tech Rep Ser. 1996 Jul;453:1-365.

Abstract

Nickel subsulfide is used in the manufacture of lithium batteries and is a major component in the refining of certain nickel ores. Nickel subsulfide was nominated as part of a class study of nickel compounds, for which there was little information on the toxic and carcinogenic effects of inhalation exposure. Male and female F334/N rats and B6C3F1 mice were exposed to nickel subsulfide (at least 97% pure; the mean value for the mass median aerodynamic diameter at each exposure concentration ranged from 2.0 to 2.2 mm by inhalation 6 hours per day, 5 days per week, for 16 days, 13 weeks, or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium, and mouse peripheral blood samples were analyzed for frequency of micronucleated normochromatic erythrocytes. 16-DAY STUDY IN RATS: Groups of five male and five female F344/N rats were exposed to atmospheres containing 0, 0.6, 1.2, 2.5, 5, or 10 mg nickel subsulfide/m(3) (equivalent to 0, 0.44, 0.88, 1.83, 3.65, and 7.33 mg nickel/m(3)) 6 hours per day, 5 days per week for a total of 12 exposure days during a 16-day period. Additionalmgroups of three male and three female rats were exposed to 0, 0.6, 2.5, or 10 mg/m(3) for tissue burden studies. One male exposed to 10 mg nickel subsulfide/m(3) in the core study died on day 14; all other rats survived until the end of the study. Final mean body weights and mean body weight gains of males exposed to 5 or 10 mg nickel subsulfide/m(3) and females exposed to 2.5, 5, or 10 mg/m(3) were significantly lower than those of the controls. Clinical findings of toxicity on day 5 of the study included labored respiration in 10 mg/m(3) males and 5 and 10 mg/m(3) females and dehydration in 5 and 10 mg/m(3) females. Absolute and relative lung weights of 2.5, 5, and 10 mg/m(3) males and all exposed groups of females were significantlymgreater than those of the controls, as was the absolute lung weight of 1.2 mg/m(3) males. Inflammation of the lung and atrophy of the nasal olfactory epithelium occurred in all exposed mgroups. The concentrations of nickel in the lungs of exposedmgroups of rats increased with exposure concentration (males, 7 to 67 mg nickel/g lung; females, 9 to 77 mg/g lung). 16-DAY STUDY IN MICE: Groups of five male and five female B6C3F1 mice were exposed to atmospheres containing 0, 0.6, 1.2, 2.5, 5, or 10 mg nickel subsulfide/m(3) for 6 hours per day, 5 days per week for a total of 12 exposure days during a 16-day period. Additional groups of three male and three female mice were exposed to 0, 0.6, 2.5, or 10 mg/m(3) for tissue burden studies. All male and female mice exposed to 10 mg nickel subsulfide/m(3) in the core study died before the end of the study; the death of one female was accidental. One control male, one control female, and one 1.2 mg/m(3) male also died before the end of the study. Final mean body weights and mean body weight gains of 5 mg/m(3) males were significantly lower than those of the controls. Clinical findings at day 5 included labored respiration in 10 mg/m(3) males and females. The absolute lung weight of 5 mg/m(3) males, the absolute and relative lung weights of 10 mg/m(3) males and 5 mg/m(3) females, and the relative lung weight of 10 mg/m(3) females were significantly greater than those of the controls. Inflammation of the lung occurred in 2.5, 5, and 10 mg/m(3) male and female mice, fibrosis of the lung occurred in 5 mg/m(3) males and females, and lymphoid hyperplasia of the bronchial lymph nodes and atrophy of the nasal olfactory epithelium occurred in 1.2, 2.5, 5, and 10 mg/m(3) males and females. Nickel concentrations in the lung of exposed male and female mice were greater than those of the controls (males, 10 to 20 mg nickel/g lung; females, 8 to 20 mg/g lung) 13-WEEK STUDY IN RATS: Groups of 10 male and 10 female F344/N rats were exposed to atmospheres containing 0, 0.15, 0.3, 0.6, 1.2, or 2.5 mg nickel subsulfide/m(3) (equivalent to 0, 0.11, 0.22, 0.44, 0.88, and 1.83 mg nickel/m(3)) 6 hours per day, 5 days per week for 13 weeks. Additional groups of 18 male and 18 female female rats were exposed to 0, 0.15, 0.6, or 2.5 mg/m(3) for tissue burden studies. All core study rats survived until the end of the study. Final mean body weights and mean body weight gains of 2.5 mg/m(3) males were significantly lower than those of the controls; final mean body weights of all other exposure groups were similar to those of the controls. Chemical-related clinical findings included labored respiration in 2.5 mg/m(3) males and females during weeks 2 through 7. In general, neutrophil and erythrocyte counts, hematocrit values, and hemoglobin concentrations were minimally increased in exposed rats. Absolute and relative lung weights of all exposed groups were significantly greater than those of the controls. Increases in the number of alveolar macrophages, interstitial infiltrates, or incidences of chronic inflammation of the lung occurred in all groups exposed to nickel subsulfide concentrations of 0.3 mg/m(3) or greater; the severity of these lesions generally increased with increasing exposure concentration. Increases in the number of alveolar macrophages were observed in 0.15 mg/m(3) males and females. Lymphoid hyperplasia of the bronchial and mediastinal lymph nodes was observed in rats exposed to 0.3 mg/m(3) or greater. Most 0.6, 1.2, and 2.5 mg/m(3) males and females had atrophy of the nasal olfactory epithelium, and the severity generally increased with increasing exposure concentration. Nickel concentrations in the lung increased with exposure concentration and were greater than those in the controls in rats exposed for 13 weeks (males, 5 to 18 mg nickel/g lung; females, 5 to 17 mg/g lung). 13-WEEK STUDY IN MICE: Groups of 10 male and 10 female B6C3F1 mice were exposed to atmospheres containing 0, 0.15, 0.3, 0.6, 1.2, or 2.5 mg nickel subsulfide/m(3) for 6 hours per day, 5 days per week for 13 weeks. Additional groups of six male and six female mice were exposed to 0, 0.15, 0.6, or 2.5 mg/m(3) for tissue burden studies. Final mean body weights of all exposure groups were similar to those of the controls. No chemical-related clinical findings were observed. Lymphocyte counts in 1.2 and 2.5 mg/m(3) males were minimally greater than that of the controls. Hemoglobin concentrations and erythrocyte counts in 0.3, 0.6, 1.2, and 2.5 mg/m(3) females were minimally greater than those of the controls. Absolute and relative lung weights of 1.2 and 2.5 mg/m(3) males and females were significantly greater than those of the controls. An increase in alveolar macrophages was present in mice from the 0.3 mg/m(3) and higher exposure groups. Chronic inflammation and fibrosis were observed in the lung of 1.2 and 2.5 mg/m(3) males and females. Interstitial infiltrates of lymphocytes were observed in mice exposed to 0.6, 1.2, or 2.5 mg/m(3). Lymphoid hyperplasia of the bronchial lymph nodes was observed in groups exposed to 1.2 or 2.5 mg/m(3). Atrophy of the nasal olfactory epithelium occurred in 0.6, 1.2, and 2.5 mg/m(3) males and females, and incidences and severity generally increased with increasing exposure concentration. At 13 weeks, nickel concentrations in the lungs of exposed mice were greater than those of the controls (males, 3 to 17 g nickel/g lung; females, 6 to 23 mg/g lung), and these concentrations increased with increasing exposure concentration. 2-YEAR STUDY IN RATS: Survival, Body Weights, Clinical Findings, and Hematology: Groups of 63 male and 63 female F344/N rats were exposed to 0, 0.15, or 1 mg nickel subsulfide/m(3) (equivalent to 0, 0.11, or 0.73 mg nickel/m(3)) by inhalation for 6 hours per day, 5 days per week for 104 weeks. Survival of exposed males and female rats was similar to that of the controls. Mean body weights of males and females exposed to 0.15 mg/m(3) were similar to those of the controls. Mean body weights of rats exposed to 1 mg/m(3) were lower than those of the controls throughout the second year of the study. Chemical-related clinical findings included rapid and shallow breathing following exposure periods. Hematocrit values and hemoglobin concentrations in 1 mg/m(3) males and females and the erythrocyte count in 1 mg/m(3) males were mildly greater than those in the controls. Pathology Findings: In general, the absolute and relative lung weights of exposed males and females were significantly greater than those of the controls at 7 and 15 months. There were exposure-related increases in the incidences of alveolar/bronchiolar adenoma in males, alveolar/bronchiolar carcinoma in males and females, and alveolar/bronchiolar adenoma or carcinoma (combined) in males and females at 2 years. Nonneoplastic lung lesions generally observed in exposed males and females included fibrosis; chronic active inflammation; focal alveolar epithelial hyperplasia, macrophage hyperplasia, and proteinosis; bronchial lymphoid hyperplasia; and interstitial inflammation. At 2 years, there were significant exposure-related increases in the incidences of benign pheochromocytoma, malignant pheochromocytoma, and benign or malignant pheochromocytoma (combined) in males and of benign pheochromocytoma in females. The incidence of adrenal medulla hyperplasia in 1 mg/m(3) females was significantly greater than that of the controls At 2 years, the incidences of chronic active inflammation of the nose in 1 mg/m(3) females and of olfactory epithelial atrophy in 1 mg/m(3) males and females were significantly greater than those of the controls. The incidences of lymphoid hyperplasia of the bronchial lymph node in exposed males at 7 and 15 months and in exposed males and females at 2 years were significantly greater than those of the controls. Incidences of macrophage hyperplasia in the bronchial lymph node of exposed males at 15 months and exposed males and females at 2 years were greater than those of the controls. Tissue Burden Analyses: Nickel concentrations in the lungs of exposed rats were greater than those of the controls at 7 months (males, 6 to 9 mg nickel/g lung; females, 6 to 9 mg/g lung) and 15 months (males, 4 to 3 mg nickel/g lung; females, 4 to 7 mg/g lung). 2-YEAR STUDY IN MICE: Survival, Body Weights, Clinical Findings, and Hematology: Groups of 80 male and 80 female B6C3F1 mice were exposed to 0, 0.6, or 1.2 mg nickel subsulfide/m(3) (equivalent to 0, 0.44, or 0.88 mg nickel/m(3)) by inhalation for 6 hours per day, 5 days per week for 105 weeks. Survival of exposed male and female mice was similar to that of the controls. Mean body weights of 0.6 and 1.2 mg/m(3) males and females were less than those of the controls throughout the second year of the study. Chemical-related clinical findings in male and female mice included labored respiration following exposure periods. The hematocrit value and the segmented neutrophil, monocyte, lymphocyte, and total leukocyte counts in 1.2 mg/m(3) females were greater than those in the controls. Pathology Findings: Absolute and relative lung weights of exposed males and females were generally significantly greater than those of the controls at 7 and 15 months. The incidence of alveolar/bronchiolar carcinoma in 0.6 mg/m(3) females and the incidences of alveolar/bronchiolar adenoma or carcinoma (combined) in 0.6 mg/m(3) males and 0.6 and 1.2 mg/m(3) females were significantly less than those of the controls. In general, the incidences of chronic active inflammation; bronchialization (alveolar epithelial hyperplasia), macrophage hyperplasia and proteinosis; interstitial infiltration; and fibrosis in exposed groups of males and females were greater than those of the controls at 7 and 15 months and at 2 years. The incidences of atrophy of the nasal olfactory epithelium and inflammation of the nose in exposed mice were also generally greater than those of the controls. At 2 years, the incidences of degeneration of olfactory epithelium in exposed females were significantly less than that of the controls. The incidences of lymphoid hyperplasia of the bronchial lymph node in 1.2 mg/m(3) males at 15 months, in 0.6 and 1.2 mg/m(3) females at 15 months, and in 0.6 and 1.2 mg/m(3) males and females at 2 years were significantly greater than those of the controls. The incidences of macrophage hyperplasia in 1.2 mg/m(3) males at 7 and 15 months, in 0.6 and 1.2 mg/m(3) females at 15 months, and in 0.6 and 1.2 mg/m(3) males and females at 2 years were significantly greater than those of the controls. Tissue Burden Analyses: Nickel concentrations in the lungs of exposed mice were greater than those of the controls at 7 months (males, 10 to 11 mg nickel/g lung; females, 10 to 14 mg/g lung) and 15 months (males, 12 to 20 mg nickel/g lung; females, 15 to 26 mg/g lung). GENETIC TOXICOLOGY: Nickel subsulfide was considered to be equivocal in the Salmonella gene mutation assay overall. Sporadic weakly positive and equivocal responses were obtained in strain TA100 with and without S9 metabolic activation enzymes; all other strain/activation combinations gave negative results. No increase in the frequency of micronucleated erythrocytes was observed in peripheral blood samples from male or female mice exposed to nickel subsulfide by inhalation for 13 weeks. CONCLUSIONS: Under the conditions of these 2-year inhalation studies, there was clear evidence of carcinogenic activity of nickel subsulfide in male F344/N rats based on increased incidences of alveolar/bronchiolar adenoma, carcinoma, and adenoma or carcinoma (combined) and on increased incidences of benign, malignant, and benign or malignant (combined) pheochromocytoma of the adrenal medulla. There was clear evidence of carcinogenic activity of nickel subsulfide in female F344/N rats based on increased incidences of alveolar/bronchiolar carcinoma and alveolar/bronchiolar adenoma or carcinoma (combined) and an increased incidence of benign pheochromocytoma of the adrenal medulla. There was no evidence of carcinogenic activity of nickel subsulfide in male or female B6C3F1 mice exposed to 0.6 or 1.2 mg/m(3). Exposure of male and female rats to nickel subsulfide by inhalation for 2 years resulted in inflammation, hyperplasia, and fibrosis in the lung; inflammation and atrophy of the olfactory epithelium in the nose; and hyperplasia in the adrenal medulla (females). Exposure of male and female mice to nickel subsulfide by inhalation for 2 years resulted in inflammation, bronchialization, hyperplasia, and fibrosis in the lung and inflammation and atrophy of the olfactory epithelium in the nose. Synonyms: Heazlewoodite, nickel subsulphide, nickel sulfide (3:2), a-nickel sulfide (3:2) crystalline, nickel sulphide, nickel tritadisulphide, trinickel disulfide

摘要

硫化亚镍用于制造锂电池,是某些镍矿精炼过程中的主要成分。硫化亚镍作为镍化合物类别研究的一部分被提名,关于吸入暴露的毒性和致癌作用,相关信息很少。将雄性和雌性F334/N大鼠以及B6C3F1小鼠暴露于硫化亚镍(纯度至少为97%;每个暴露浓度下质量中位空气动力学直径的平均值范围为2.0至2.2毫米),每天吸入6小时,每周5天,持续16天、13周或2年。在鼠伤寒沙门氏菌中进行了遗传毒理学研究,并对小鼠外周血样本进行了微核正常红细胞频率分析。

大鼠16天研究:将每组5只雄性和5只雌性F344/N大鼠暴露于含有0、0.6、1.2、2.5、5或10毫克硫化亚镍/立方米(相当于0、0.44、0.88、1.83、3.65和7.33毫克镍/立方米)的环境中,每天6小时,每周5天,在16天内共暴露12天。另外,每组3只雄性和3只雌性大鼠暴露于0、0.6、2.5或10毫克/立方米的环境中进行组织负荷研究。核心研究中,一只暴露于10毫克硫化亚镍/立方米的雄性大鼠在第14天死亡;所有其他大鼠存活至研究结束。暴露于5或10毫克硫化亚镍/立方米的雄性大鼠以及暴露于2.5、5或10毫克/立方米的雌性大鼠的最终平均体重和平均体重增加量显著低于对照组。研究第5天的毒性临床表现包括,暴露于10毫克/立方米的雄性大鼠以及暴露于5和10毫克/立方米的雌性大鼠出现呼吸急促,暴露于5和10毫克/立方米的雌性大鼠出现脱水。暴露于2.5、5和10毫克/立方米的雄性大鼠以及所有暴露组的雌性大鼠的绝对和相对肺重量显著高于对照组,暴露于1.2毫克/立方米的雄性大鼠的绝对肺重量也是如此。所有暴露组均出现肺部炎症和鼻嗅上皮萎缩。暴露组大鼠肺部的镍浓度随暴露浓度增加而升高(雄性,7至67毫克镍/克肺;雌性,9至77毫克/克肺)。

小鼠16天研究:将每组5只雄性和5只雌性B6C3F1小鼠暴露于含有0、0.6、1.2、2.5、5或10毫克硫化亚镍/立方米的环境中,每天6小时,每周5天,在16天内共暴露12天。另外,每组3只雄性和3只雌性小鼠暴露于0、0.6、2.5或10毫克/立方米的环境中进行组织负荷研究。核心研究中,所有暴露于10毫克硫化亚镍/立方米的雄性和雌性小鼠在研究结束前死亡;一只雌性小鼠的死亡是意外情况。一只对照雄性、一只对照雌性和一只暴露于1.2毫克/立方米的雄性小鼠也在研究结束前死亡。暴露于5毫克/立方米的雄性小鼠的最终平均体重和平均体重增加量显著低于对照组。第5天的临床表现包括,暴露于10毫克/立方米的雄性和雌性小鼠出现呼吸急促。暴露于5毫克/立方米的雄性小鼠的绝对肺重量、暴露于10毫克/立方米的雄性和暴露于5毫克/立方米的雌性小鼠的绝对和相对肺重量,以及暴露于10毫克/立方米的雌性小鼠的相对肺重量均显著高于对照组。暴露于2.5、5和10毫克/立方米的雄性和雌性小鼠出现肺部炎症,暴露于5毫克/立方米的雄性和雌性小鼠出现肺部纤维化,暴露于1.2、2.5、5和10毫克/立方米的雄性和雌性小鼠出现支气管淋巴结淋巴样增生和鼻嗅上皮萎缩。暴露的雄性和雌性小鼠肺部的镍浓度高于对照组(雄性,10至20毫克镍/克肺;雌性,8至20毫克/克肺)。

大鼠13周研究:将每组10只雄性和10只雌性F344/N大鼠暴露于含有0、0.15、0.3、0.6、1.2或2.5毫克硫化亚镍/立方米(相当于0、0.11、0.22、0.44、0.88和1.83毫克镍/立方米)的环境中,每天6小时,每周5天,持续13周。另外,每组1八只雄性和1八只雌性大鼠暴露于0、0.15、0.6或2.5毫克/立方米的环境中进行组织负荷研究。所有核心研究大鼠存活至研究结束。暴露于2.5毫克/立方米的雄性大鼠的最终平均体重和平均体重增加量显著低于对照组;所有其他暴露组的最终平均体重与对照组相似。与化学物质相关的临床表现包括,在第2至7周,暴露于2.5毫克/立方米的雄性和雌性大鼠出现呼吸急促。一般来说,暴露大鼠的中性粒细胞和红细胞计数、血细胞比容值和血红蛋白浓度略有增加。所有暴露组的绝对和相对肺重量均显著高于对照组。暴露于0.3毫克/立方米或更高浓度硫化亚镍的所有组均出现肺泡巨噬细胞数量增加、间质浸润或肺部慢性炎症发生率增加;这些病变的严重程度通常随暴露浓度增加而增加。在暴露于0.15毫克/立方米的雄性和雌性大鼠中观察到肺泡巨噬细胞数量增加。在暴露于0.3毫克/立方米或更高浓度的大鼠中观察到支气管和纵隔淋巴结淋巴样增生。大多数暴露于0.6、1.2和2.5毫克/立方米的雄性和雌性大鼠出现鼻嗅上皮萎缩,其严重程度通常随暴露浓度增加而增加。暴露13周的大鼠肺部的镍浓度随暴露浓度增加而升高,且高于对照组(雄性,5至18毫克镍/克肺;雌性,5至17毫克/克肺)。

小鼠13周研究:将每组10只雄性和10只雌性B6C3F1小鼠暴露于含有0、0.15、0.3、0.6、1.2或2.5毫克硫化亚镍/立方米的环境中,每天6小时,每周5天,持续13周。另外,每组6只雄性和6只雌性小鼠暴露于0、0.15、0.6或2.5毫克/立方米的环境中进行组织负荷研究。所有暴露组的最终平均体重与对照组相似。未观察到与化学物质相关的临床表现。暴露于1.2和2.5毫克/立方米的雄性大鼠的淋巴细胞计数略高于对照组。暴露于0.3、0.6、1.2和2.5毫克/立方米的雌性大鼠的血红蛋白浓度和红细胞计数略高于对照组。暴露于1.2和2.5毫克/立方米的雄性和雌性小鼠的绝对和相对肺重量均显著高于对照组。在暴露于0.3毫克/立方米及更高浓度的小鼠中出现肺泡巨噬细胞数量增加。在暴露于1.2和2.5毫克/立方米的雄性和雌性小鼠的肺部观察到慢性炎症和纤维化。在暴露于0.6、1.2或2.5毫克/立方米的小鼠中观察到淋巴细胞间质浸润。在暴露于1.2或2.5毫克/立方米的组中观察到支气管淋巴结淋巴样增生。在暴露于0.6、1.2和2.5毫克/立方米的雄性和雌性小鼠中出现鼻嗅上皮萎缩,其发生率和严重程度通常随暴露浓度增加而增加。在13周时,暴露小鼠肺部的镍浓度高于对照组(雄性,3至17微克镍/克肺;雌性,6至23毫克/克肺),且这些浓度随暴露浓度增加而升高。

大鼠两年研究

生存、体重、临床表现和血液学:将每组63只雄性和63只雌性F344/N大鼠暴露于0、0.15或1毫克硫化亚镍/立方米(相当于0、0.11或0.73毫克镍/立方米)的环境中,每天吸入6小时,每周5天,持续104周。暴露的雄性和雌性大鼠的存活率与对照组相似。暴露于0.15毫克/立方米的雄性和雌性大鼠的平均体重与对照组相似。在研究的第二年,暴露于1毫克/立方米的大鼠的平均体重低于对照组。与化学物质相关的临床表现包括暴露期后呼吸急促且浅表。暴露于1毫克/立方米的雄性和雌性大鼠的血细胞比容值和血红蛋白浓度以及暴露于1毫克/立方米的雄性大鼠的红细胞计数略高于对照组。

病理学发现

一般来说,在7个月和15个月时,暴露的雄性和雌性大鼠的绝对和相对肺重量显著高于对照组。在2年时,雄性大鼠的肺泡/细支气管腺瘤、雄性和雌性大鼠的肺泡/细支气管癌以及雄性和雌性大鼠的肺泡/细支气管腺瘤或癌(合并)的发生率与暴露有关增加。暴露的雄性和雌性大鼠中普遍观察到的非肿瘤性肺部病变包括纤维化;慢性活动性炎症;局灶性肺泡上皮增生、巨噬细胞增生和蛋白沉积;支气管淋巴样增生;以及间质炎症。在2年时,雄性大鼠的良性嗜铬细胞瘤、恶性嗜铬细胞瘤以及良性或恶性嗜铬细胞瘤(合并)的发生率与暴露有关显著增加,雌性大鼠的良性嗜铬细胞瘤发生率也与暴露有关显著增加。暴露于1毫克/立方米的雌性大鼠的肾上腺髓质增生发生率显著高于对照组。在2年时,暴露于1毫克/立方米的雌性大鼠的鼻部慢性活动性炎症发生率以及暴露于1毫克/立方米的雄性和雌性大鼠的嗅上皮萎缩发生率显著高于对照组。在7个月和15个月时,暴露雄性大鼠的支气管淋巴结淋巴样增生发生率以及在2年时暴露雄性和雌性大鼠的支气管淋巴结淋巴样增生发生率显著高于对照组。在15个月时,暴露雄性大鼠的支气管淋巴结巨噬细胞增生发生率以及在2年时暴露雄性和雌性大鼠的支气管淋巴结巨噬细胞增生发生率高于对照组。

组织负荷分析

在7个月时(雄性,6至9毫克镍/克肺;雌性,6至9毫克镍/克肺)和15个月时(雄性,4至3毫克镍/克肺;雌性,4至7毫克镍/克肺),暴露大鼠肺部的镍浓度高于对照组。

小鼠两年研究

生存、体重、临床表现和血液学:将每组80只雄性和80只雌性B6C3F1小鼠暴露于0、0.6或1.2毫克硫化亚镍/立方米(相当于0、0.44或0.88毫克镍/立方米)的环境中,每天吸入6小时,每周5天,持续105周。暴露的雄性和雌性小鼠的存活率与对照组相似。在研究的第二年,暴露于0.6和1.2毫克/立方米的雄性和雌性小鼠的平均体重低于对照组。雄性和雌性小鼠与化学物质相关的临床表现包括暴露期后呼吸急促。暴露于1.2毫克/立方米的雌性大鼠的血细胞比容值、分叶中性粒细胞、单核细胞、淋巴细胞和总白细胞计数高于对照组。

病理学发现

在7个月和15个月时,暴露的雄性和雌性小鼠的绝对和相对肺重量通常显著高于对照组。暴露于0.6毫克/立方米的雌性小鼠的肺泡/细支气管癌发生率以及暴露于0.6毫克/立方米的雄性小鼠和暴露于0.6和1.2毫克/立方米的雌性小鼠的肺泡/细支气管腺瘤或癌(合并)发生率显著低于对照组。一般来说,在7个月、15个月和2年时,暴露组的雄性和雌性小鼠的慢性活动性炎症、支气管化生(肺泡上皮增生)、巨噬细胞增生和蛋白沉积、间质浸润以及纤维化的发生率高于对照组。暴露小鼠的鼻嗅上皮萎缩和鼻部炎症的发生率也通常高于对照组。在2年时,暴露雌性小鼠的嗅上皮变性发生率显著低于对照组。在15个月时,暴露于1.2毫克/立方米的雄性小鼠、在15个月时暴露于0.6和1.2毫克/立方米的雌性小鼠以及在2年时暴露于0.6和1.2毫克/立方米的雄性和雌性小鼠的支气管淋巴结淋巴样增生发生率显著高于对照组。在7个月和15个月时,暴露于1.2毫克/立方米的雄性小鼠、在15个月时暴露于0.6和1.2毫克/立方米

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