Department of Environmental Engineering, Peking University, The Key Laboratory of Water and Sediment Sciences, Ministry of Education, Beijing 100871, China.
Department of Civil and Environmental Engineering, University of Washington, Box 352700, Seattle, WA 98195-2700, United States.
Water Res. 2014 Mar 1;50:179-88. doi: 10.1016/j.watres.2013.11.028. Epub 2013 Dec 4.
Formation of disinfection by-products (DBPs) in ten drinking source waters located in the United States was examined in this study. DBP generation was interpreted in the context of halogenation-induced changes of log-transformed absorbance spectra of dissolved organic matter (DOM) present in the waters. This approach allows probing the behavior of relatively minor structures that can be highly sensitive towards any process of interest, notably DOM halogenation. This concept was applied to examine effects of chlorination time on the kinetics of chlorine consumption and release of several DBP groups such as total trihalomethanes (THM4, including CHCl3, CHCl2Br, CHClBr2 and CHBr3), haloacetic acids (HAA9, including MCAA, MBAA, DCAA, TCAA, BCAA, DBAA, BDCAA, DBCAA and TBAA), haloacetonitriles (THAN4, including TCAN, DCAN, BCAN and DBAN), haloketones (HK2, including DCP and TCP), chloral hydrate (CH) and chloropicrin (CPN). Two alternative parameters, namely the differential logarithm of DOM absorbance at 350 nm (DLnA350) and change of the spectral slope in the range of wavelengths 325-375 nm (DSlope325-375) were introduced to quantify individual DBP species formed and Cl2 consumption. DLnA350 and DSlope325-375, especially DLnA350 were determined to be more reliable than differential absorbance at 272 nm that was utilized in prior applications of differential spectroscopy to characterize DBP formation. Strong linear relationships between DLnA350 values and concentrations of major groups of and individual DBP species (e.g. THM4, HAA9, HAN4 and CPN were found to exist (mostly, R(2) > 0.95) and the intercept of these correlations with the y-axis was near zero for the examined water sources. Correlations between DLnA350 values and concentrations of CH and HK2 were also strong but they were nonlinear. The slope of the correlations between the concentrations of major groups of DBP species vs -DLnA350 were also well correlated with SUVA254 and LnA350 for all the examined source waters. It indicates that log-transformations of the absorbance spectra of surface water and parameters based on such transformations (e.g., DLnA350 and DSlope325-375) have a potential to provide an alternative reliable approach to monitor the halogenation of DOM and attendant formation of individual DBP species.
本研究考察了美国十个饮用水源中消毒副产物(DBP)的形成情况。DBP 的生成是通过卤化诱导的水中溶解有机物(DOM)的对数转换吸光度光谱变化来解释的。这种方法可以探测到相对较小结构的行为,这些结构对任何感兴趣的过程都非常敏感,特别是 DOM 卤化。该概念用于研究氯化时间对氯消耗动力学和几种 DBP 组(例如总三卤甲烷(THM4,包括 CHCl3、CHCl2Br、CHClBr2 和 CHBr3)、卤乙酸(HAA9,包括 MCAA、MBAA、DCAA、TCAA、BCAA、DBAA、BDCAA、DBCAA 和 TBAA)、卤乙腈(THAN4,包括 TCAN、DCAN、BCAN 和 DBAN)、卤代酮(HK2,包括 DCP 和 TCP)、三氯乙醛(CH)和氯仿(CPN))的释放的影响。引入了两个替代参数,即 350nm 处 DOM 吸光度的差分对数(DLnA350)和波长 325-375nm 范围内光谱斜率的变化(DSlope325-375),以量化形成的单个 DBP 物种和 Cl2 的消耗。DLnA350 和 DSlope325-375,特别是 DLnA350,被确定比先前差分光谱应用中用于表征 DBP 形成的 272nm 差分吸光度更可靠。在研究的水源中,发现 DLnA350 值与主要 DBP 物种(如 THM4、HAA9、HAN4 和 CPN)的浓度之间存在很强的线性关系(大多数情况下,R2>0.95),这些相关性与 y 轴的截距接近零。DLnA350 值与 CH 和 HK2 浓度之间的相关性也很强,但呈非线性。主要 DBP 物种浓度与-DLnA350 之间的相关性的斜率也与所有研究水源的 SUVA254 和 LnA350 密切相关。这表明地表水吸光度光谱的对数转换以及基于这些转换的参数(例如,DLnA350 和 DSlope325-375)有可能提供一种替代的可靠方法来监测 DOM 的卤化和伴随的单个 DBP 物种的形成。