College of Environmental Science and Engineering, Tongji University, Shanghai 200092, China.
J Environ Sci (China). 2012;24(7):1204-9. doi: 10.1016/s1001-0742(11)61006-1.
This work investigated the formation of carbonaceous and nitrogenous disinfection by-products (C-DBPs, N-DBPs) upon chlorination of water samples collected from a surface water and a ground water treatment plant (SWTP and GWTP) where the conventional treatment processes, i.e., coagulation, sedimentation, and filtration were employed. Twenty DBPs, including four trihalomethanes, nine haloacetic acids, seven N-DBPs (dichloroacetamide, trichloroacetamide, dichloroacetonitrile, trichloroacetonitrile, bromochloroacetonitrile, dibromoacetonitrile and trichloronitromethane), and eight volatile chlorinated compounds (dichloromethane (DCM), 1,2-dichloroethane, tetrachloroethylene, chlorobenzene, 1,2-dichlorobenzene, 1,4-dichlorobenzene, 1,2,3-trichlorobenzene and 1,2,4-trichlorobenzene) were detected in the two WTPs. The concentrations of these contaminants were all below their corresponding maximum contamination levels (MCLs) regulated by the Standards for Drinking Water Quality of China (GB5749-2006) except for DCM (17.1 microg/L detected vs. 20 microg/L MCL). The SWTP had much higher concentrations of DBPs detected in the treated water as well as the DBP formation potentials tested in the filtered water than the GWTP, probably because more precursors (e.g., dissolved organic carbon, dissolved organic nitrogen) were present in the water source of the SWTP.
本研究考察了地表水和地下水处理厂(SWTP 和 GWTP)水样在氯化过程中碳质和氮质消毒副产物(C-DBPs、N-DBPs)的形成情况。在这两个处理厂中,采用了常规处理工艺,包括混凝、沉淀和过滤。检测到 20 种 DBPs,包括四种三卤甲烷、九种卤乙酸、七种 N-DBPs(二氯乙酰胺、三氯乙酰胺、二氯乙腈、三氯乙腈、溴氯乙腈、二溴乙腈和三氯硝基甲烷)和八种挥发性氯化物(二氯甲烷(DCM)、1,2-二氯乙烷、四氯乙烯、氯苯、1,2-二氯苯、1,4-二氯苯、1,2,3-三氯苯和 1,2,4-三氯苯)。除 DCM(检出浓度为 17.1μg/L,而中国《生活饮用水卫生标准》(GB5749-2006)规定的最大浓度限值为 20μg/L)外,这些污染物的浓度均低于相应的最大浓度限值。SWTP 处理后的水中以及过滤水中的 DBPs 浓度以及 DBP 生成潜能均高于 GWTP,这可能是因为 SWTP 水源中存在更多的前体物质(如溶解有机碳、溶解有机氮)。