CD大鼠和CD-1小鼠对苯乙烯的亚慢性吸入研究。

G. Cruzan, JANETTE R. Cushman, LARRY S. Andrews, GEOFFREY C. Granville, ROLAND R. Miller, COLIN J. Hardy, D. W. Coombs, Pamela A. Mullins
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引用次数: 71

摘要

每组10只雄性和10只雌性查尔斯河(CRL) CD (spraguale - dawley衍生)大鼠暴露于0、200、500、1000或1500 ppm浓度的苯乙烯蒸汽中,每天6小时,每周5天,持续13周。苯乙烯对生存、血液学或临床化学没有影响。浓度为1500ppm的男性在13周后体重减轻10%,浓度为1000和1500ppm的男性和女性比对照组消耗更多的水。组织病理学改变局限于鼻黏膜的嗅上皮。每组20只雄性和20只雌性CRL CD-1和B6C3F1小鼠暴露于0、15、60、250或500 ppm浓度的苯乙烯蒸汽中,每天6小时,每周5天,持续2周。暴露于250或500 ppm的CD-1和B6C3F1小鼠均观察到死亡;暴露在PPM浓度为250的环境中比暴露在PPM浓度为500的环境中死亡的雌性老鼠更多,但雄性老鼠没有。每组10只雄性和10只雌性CRL CD-1小鼠暴露于0、50、100、150或200 ppm浓度的苯乙烯蒸汽中,每天6小时,每周5天,持续13周。两名接触到200ppm的女性在第一周死亡。在200 ppm时,死者和一些女性幸存者的肝脏毒性很明显。在暴露于100,150或200ppm的小鼠肺部和所有治疗组的鼻腔通道中观察到变化,暴露于50ppm的小鼠受影响较小。卫星组15只雄性大鼠和30只雄性小鼠按上述方法暴露2、5或13周,测量细胞增殖(BrdU标记)。大鼠、小鼠肝脏及大鼠肺细支气管、肺泡区细胞增殖均未见增加。小鼠肺中II型肺细胞的标记指数未见增加,而在150和200 ppm时,Clara细胞的标记指数在2周后增加,在5周后偶见小鼠。动物之间标注指数的巨大差异强调了大群体规模的必要性。对于鼻道效应,CD-1小鼠未发现NOAEL,但在CD大鼠中,NOAEL为200 ppm。对于其他影响,NOAEL在大鼠中为500ppm,在小鼠中为50ppm。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Subchronic inhalation studies of styrene in CD rats and CD-1 mice.
Groups of 10 male and 10 female Charles River (CRL) CD (Sprague-Dawley-derived) rats were exposed to styrene vapor at 0, 200, 500, 1000, or 1500 ppm 6 hr per day 5 days per week for 13 weeks. Styrene had no effect on survival, hematology, or clinical chemistry. Males at 1500 ppm weighed 10% less after 13 weeks and males and females at 1000 and 1500 ppm consumed more water than controls. Histopathologic changes were confined to the olfactory epithelium of the nasal mucosa. Groups of 20 male and 20 female CRL CD-1 and B6C3F1 mice were exposed to styrene vapor at 0, 15, 60, 250, or 500 ppm 6 hr per day 5 days per week for 2 weeks. Mortality was observed in both CD-1 and B6C3F1 mice exposed to 250 or 500 ppm; more female mice, but not males, died from exposure to 250 ppm than from 500 ppm. Groups of 10 male and 10 female CRL CD-1 mice were exposed to styrene vapors at 0, 50, 100, 150, or 200 ppm 6 hr per day 5 days per week for 13 weeks. Two females exposed to 200 ppm died during the first week. Liver toxicity was evident in the decedents and in some female survivors at 200 ppm. Changes were observed in the lungs of mice exposed to 100, 150, or 200 ppm and in the nasal passages of all treatment groups, those exposed to 50 ppm being less affected. Satellite groups of 15 male rats and 30 male mice were exposed as described above for 2, 5, or 13 weeks for measurement of cell proliferation (BrdU labeling). No increase in cell proliferation was found in liver of rats or mice or in cells of the bronchiolar or alveolar region of the lung of rats. No increase in labeling index of type II pneumocytes was seen in mouse lungs, while at 150 and 200 ppm, an increased labeling index of Clara cells was seen after 2 weeks and in occasional mice after 5 weeks. Large variations in the labeling index among animals emphasize the need for large group sizes. For nasal tract effects, a NOAEL was not found in CD-1 mice, but in CD rats, the NOAEL was 200 ppm. For other effects, the NOAEL was 500 ppm in rats and 50 ppm in mice.
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