Meier J R
Toxicology and Microbiology Division, U.S. Environmental Protection Agency, Cincinnati, OH 45268.
Mutat Res. 1988 Nov;196(3):211-45. doi: 10.1016/0165-1110(88)90008-5.
The information summarized in this review provides substantial evidence for the widespread presence of genotoxins in drinking water. In many, if not most cases, the genotoxic activity can be directly attributed to the chlorination stage of drinking water treatment. The genotoxic activity appears to originate primarily from reactions of chlorine with humic substances in the source waters. Genotoxic activity in drinking water concentrates has been most frequently demonstrated using bacterial mutagenicity tests but results with mammalian cell assay systems are generally consistent with the findings from the bacterial assays. There is currently no evidence for genotoxic damage following in vivo exposures to animals. In some locations genotoxic contaminants of probable industrial and/or agricultural origin occur in the source waters and contribute substantially to the genotoxic activity of finished drinking waters. The method used for sample concentration can have an important bearing on study results. In particular, organic acids account for most of the mutagenicity of chlorinated drinking water, and their recovery from water requires a sample acidification step prior to extraction or XAD resin adsorption. Considerable work has been done to determine the identity of the compounds responsible for the mutagenicity of organic concentrates of drinking water. Recently, one class of acidic compounds, the chlorinated hydroxyfuranones, has been shown to be responsible for a major part of the mutagenic activity. Strategies for drinking water treatment that have been evaluated with respect to reduction of genotoxins in drinking water include granular activated carbon (GAC) filtration, chemical destruction, and the use of alternative means of treatment (i.e., ozone, chlorine dioxide, and monochloramine). GAC treatment has been found to be effective for removal of mutagens from drinking water even after the GAC is beyond its normal use for organic carbon removal. All disinfectant chemicals appear to have the capacity of forming mutagenic chemicals during water treatment. However, the levels of mutagenicity formed with the alternative disinfectants have been generally less than those seen with chlorine and, especially in the case of ozone, highly dependent on the source water.(ABSTRACT TRUNCATED AT 400 WORDS)
本综述中总结的信息为饮用水中广泛存在基因毒素提供了大量证据。在许多情况下(即便不是大多数情况),基因毒性活性可直接归因于饮用水处理的氯化阶段。基因毒性活性似乎主要源于氯与源水中腐殖质的反应。饮用水浓缩物中的基因毒性活性最常通过细菌致突变性试验得到证实,但哺乳动物细胞检测系统的结果通常与细菌检测结果一致。目前尚无证据表明动物体内暴露后会出现基因毒性损伤。在一些地方,源水中存在可能源自工业和/或农业的基因毒性污染物,这些污染物对成品饮用水的基因毒性活性有很大影响。用于样品浓缩的方法可能对研究结果有重要影响。特别是,有机酸占氯化饮用水致突变性的大部分,从水中回收它们需要在萃取或XAD树脂吸附之前进行样品酸化步骤。为确定导致饮用水有机浓缩物致突变性的化合物身份已开展了大量工作。最近,一类酸性化合物,即氯化羟基呋喃酮,已被证明是致突变活性的主要原因。已针对减少饮用水中基因毒素进行评估的饮用水处理策略包括颗粒活性炭(GAC)过滤、化学破坏以及使用替代处理方法(即臭氧、二氧化氯和一氯胺)。已发现GAC处理对于去除饮用水中的诱变剂有效,即使GAC超出其正常去除有机碳的用途。所有消毒化学品在水处理过程中似乎都有形成诱变化学品的能力。然而,使用替代消毒剂形成的致突变性水平通常低于使用氯时的水平,特别是在臭氧的情况下,高度依赖于源水。(摘要截断于400字)