Moudgal C J, Lipscomb J C, Bruce R M
National Center for Environmental Assessment, U.S. Environmental Protection Agency, Cincinnati, OH 45268, USA.
Toxicology. 2000 Jun 8;147(2):109-31. doi: 10.1016/s0300-483x(00)00188-8.
Disinfection by-products (DBPs) are produced as a result of disinfecting water using various treatment methods. Over the years, chlorine has remained the most popular disinfecting agent due to its ability to kill pathogens. However, in 1974, it was discovered that the superchlorination of drinking water resulted in the production of chloroform and other trihalomethanes. Since then hundreds of additional DBPs have been identified, including haloacetic acids and haloacetonitriles with very little or no toxicological data available, thus necessitating the use of additional methods for hazard estimation. Quantitative Structure Toxicity Relationship (QSTR) is one such method and utilizes a computer-based technology to predict the toxicity of a chemical solely from its molecular attributes. The current research was conducted utilizing the TOPKAT/QSTR software package which is comprised of robust, cross-validated QSTR models for assessing mutagenicity, rodent carcinogenicity (female/male; rat/mouse), developmental toxicity, skin sensitization, lowest-observed-adverse-effect level (LOAEL), fathead minnow LC(50), rat oral LD(50) and Daphia magna EC(50). A total of 252 DBPs were analyzed for the likelihood that they would produce tumors and developmental effects using the carcinogenicity and developmental toxicity submodels of TOPKAT. The model predictions were evaluated to identify generalizations between the functional groups (e.g. alcohols, acids, etc.) and specific toxic endpoints. Developmental toxicity was identified as an endpoint common to the majority of aliphatic mono- and dicarboxylic acids, aliphatic halogenated and non-halogenated ketones, and aliphatic haloacetonitriles. In the case of the carcinogenicity submodels, most aliphatic aldehydes were identified as carcinogens only in the female mouse submodel. The majority of the aliphatic and aromatic dicarboxylic acids were identified as carcinogens in the female rat submodel. All other functional groups examined were largely predicted as non-carcinogens in all the cancer submodels (i.e. male/female rats and mice). The QSTR results should aid in the prioritization for evaluation of toxic endpoints in the absence of in vivo bioassays.
消毒副产物(DBPs)是使用各种处理方法对水进行消毒的结果。多年来,由于氯具有杀灭病原体的能力,它一直是最受欢迎的消毒剂。然而,1974年人们发现,饮用水的过度氯化会导致氯仿和其他三卤甲烷的产生。从那时起,又发现了数百种其他消毒副产物,包括卤乙酸和卤乙腈,而关于它们的毒理学数据非常少或几乎没有,因此需要使用其他方法来评估危害。定量结构毒性关系(QSTR)就是这样一种方法,它利用基于计算机的技术仅根据化学物质的分子属性来预测其毒性。当前的研究使用了TOPKAT/QSTR软件包进行,该软件包由强大的、经过交叉验证的QSTR模型组成,用于评估致突变性、啮齿动物致癌性(雌性/雄性;大鼠/小鼠)、发育毒性、皮肤致敏性、最低观察到的不良反应水平(LOAEL)、黑头呆鱼LC(50)、大鼠口服LD(50)和大型溞EC(50)。使用TOPKAT的致癌性和发育毒性子模型,对总共252种消毒副产物产生肿瘤和发育影响的可能性进行了分析。对模型预测结果进行评估,以确定官能团(如醇类、酸类等)与特定毒性终点之间的普遍关系。发育毒性被确定为大多数脂肪族一元和二元羧酸、脂肪族卤代和非卤代酮以及脂肪族卤乙腈共有的终点。在致癌性子模型中,大多数脂肪族醛仅在雌性小鼠子模型中被确定为致癌物。大多数脂肪族和芳香族二元羧酸在雌性大鼠子模型中被确定为致癌物。在所有癌症子模型(即雄性/雌性大鼠和小鼠)中,所研究的所有其他官能团大多被预测为非致癌物。在没有体内生物测定的情况下,QSTR结果应有助于确定毒性终点评估的优先级。