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强效细菌诱变剂3-氯-4-(二氯甲基)-5-羟基-2(5H)-呋喃酮的研究:在饮用水和氯化腐殖酸溶液中的水稳定性、XAD回收率及分析测定

Studies on the potent bacterial mutagen, 3-chloro-4-(dichloromethyl)-5-hydroxy-2(5H)-furanone: aqueous stability, XAD recovery and analytical determination in drinking water and in chlorinated humic acid solutions.

作者信息

Meier J R, Knohl R B, Coleman W E, Ringhand H P, Munch J W, Kaylor W H, Streicher R P, Kopfler F C

机构信息

Toxicology and Microbiology Division, U.S. Environmental Protection Agency, Cincinnati, OH 45268.

出版信息

Mutat Res. 1987 Dec;189(4):363-73. doi: 10.1016/0165-1218(87)90044-9.

Abstract

3-Chloro-4-(dichloromethyl)-5-hydroxy-2(5H)-furanone (MX) was detected by gas chromatography/mass spectrometry in drinking water samples from 3 locations in the U.S.A., and also in a chlorinated humic acid solution. MX appears to account for a significant proportion of the mutagenicity of these samples, as measured in the Ames test using strain TA100 without metabolic activation. Studies on recovery of MX from spiked water samples by XAD-2/8 resin adsorption/acetone elution indicated that sample acidification prior to resin adsorption was essential to the effective recovery of MX. The stability of MX in aqueous solution was pH and temperature dependent. At 23 degrees C the order of stability, based on persistence of mutagenic activity was found to be: pH 2 greater than pH 4 greater than pH 8 greater than pH 6. The half-life at pH 8 and 23 degrees C was 4.6 days. One of the degradation products has been tentatively identified as 2-chloro-3-(dichloromethyl)-4-oxo-2-butenoic acid, an open form of MX which appears to be in the "E" configuration. Overall, these results suggest that MX is formed during water chlorination as a result of reaction of chlorine with humic substances, and that a substantial fraction of the MX formed is likely to persist throughout the distribution system.

摘要

采用气相色谱/质谱法在美国3个地点采集的饮用水样本以及氯化腐殖酸溶液中检测到了3-氯-4-(二氯甲基)-5-羟基-2(5H)-呋喃酮(MX)。在使用TA100菌株且无代谢激活的艾姆斯试验中测定发现,MX似乎在这些样本的诱变性中占很大比例。通过XAD-2/8树脂吸附/丙酮洗脱从加标水样中回收MX的研究表明,树脂吸附前对样品进行酸化对于有效回收MX至关重要。MX在水溶液中的稳定性取决于pH值和温度。在23℃时,根据诱变活性的持久性,稳定性顺序为:pH 2>pH 4>pH 8>pH 6。在pH 8和23℃时的半衰期为4.6天。其中一种降解产物已初步鉴定为2-氯-3-(二氯甲基)-4-氧代-2-丁烯酸,它是MX的一种开环形式,似乎呈“E”构型。总体而言,这些结果表明,MX是在水氯化过程中由氯与腐殖物质反应形成的,并且所形成的大部分MX可能会在整个供水系统中持续存在。

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