1,4‐二氯苯[MAK值文件,2018]

A. Hartwig, M. Arand
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引用次数: 0

摘要

德国工作区域化学品健康危害调查委员会考虑到所有毒理学终点,重新评估了1,4 -二氯苯[106 - 46 - 7]。详细描述了可用的出版物和未发表的研究报告。在小鼠肝脏中,1,4‐二氯苯在口服和吸入后会导致癌症,并具有有丝分裂和细胞毒性。在可靠的研究中,它没有基因毒性。由于非基因毒性机制是最重要的,而基因毒性作用最多只起很小的作用,只要在工作场所观察到最大浓度(MAK值),1,4‐二氯苯现在被列为第4类致癌物质。大鼠鼻嗅上皮变化的慢性局部NOAEC为20 ml/m3,对应MAK值为10 ml/m3。然而,在对狗进行的为期52周的口服研究中,最敏感的毒理学效应是肝细胞肥大,其LOAEL为10 mg/kg体重和日。由于该效应的严重程度和发生率较低,因此假定每日5 mg/kg体重为NAEL(无不良反应水平)。该NAEL按比例缩放至MAK值为2ml /m3。由于系统效应是关键的,峰值限制类别II被指定。由于尚不清楚这种影响是由于代谢物还是1,4‐二氯苯本身造成的,因此指定了默认偏移因子2。对大鼠和家兔的发育毒性noaec分别为500和100 ml/m3,与MAK值的差异是足够的。因此,当观察到MAK值并将1,4‐二氯苯归为妊娠风险组c时,不太可能对胚胎或胎儿造成损害。皮肤接触可能对全身毒性有显著影响,而1,4‐二氯苯仍被指定为“H”标记。从有限的数据中预计不会产生致敏性。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
1,4‐Dichlorobenzene [MAK Value Documentation, 2018]
The German Commission for the investigation of Health Hazards of Chemical Compounds in the Work Area has re‐evaluated 1,4‐dichlorobenzene [106‐46‐7] considering all toxicological endpoints. Available publications and unpublished study reports are described in detail. In mouse liver, 1,4‐dichlorobenzene causes carcinoma after oral and inhalation exposure and is mitogenic and cytotoxic. In reliable studies it is not genotoxic. As a non‐genotoxic mechanism is of prime importance and genotoxic effects play at most a minor part, provided the maximum concentration at the workplace (MAK value) is observed, 1,4‐dichlororbenzene is now classified in Category 4 for carcinogenic substances. The chronic local NOAEC of 20 ml/m3 for changes in the olfactory epithelium of the rat nose would correspond to a MAK value of 10 ml/m3. However, the most sensitive toxicological effect is hepatocellular hypertrophy with a LOAEL of 10 mg/kg body weight and day in an oral 52‐week study with dogs. Because of the low severity and incidence of the effect, a NAEL (no adverse effect level) of 5 mg/kg body weight and day is assumed. This NAEL is scaled to a MAK value of 2 ml/m3. Since a systemic effect is critical, Peak Limitation Category II is assigned. As it is not known if the effects are due to the metabolites or 1,4‐dichlorobenzene itself, the default excursion factor of 2 is assigned. The NOAECs for developmental toxicity in rats and rabbits are 500 and 100 ml/m3, respectively, and the differences to the MAK value are sufficient. Therefore, damage to the embryo or foetus is unlikely when the MAK value is observed and 1,4‐dichlorobenzene is assigned to Pregnancy Risk Group C. Skin contact may contribute significantly to systemic toxicity and 1,4‐dichlorobenzene remains designated with an “H” notation. Sensitization is not expected from the limited data.
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