Hohai University, College of Environment, Nanjing 210098, China; Zhejiang Province Ecology Environmental Monitoring Center, Hangzhou 310012, China.
College of Civil Engineering, Zhejiang University of Technology, Hangzhou 310023, China.
Sci Total Environ. 2021 Jun 1;771:144885. doi: 10.1016/j.scitotenv.2020.144885. Epub 2021 Jan 28.
Dissolved nitrogenous organic matter in water can contain precursors of disinfection by-products (DBPs), especially nitrogenous DBPs (N-DBPs). Amino acids are ubiquitous as dissolved nitrogenous organic matter in source water and can pass through drinking water treatment processes to react with disinfectants in finished water and in the distribution system. Phenylalanine (Phe) was selected as a model amino acid precursor to investigate its derived DBPs and their variations during a chlorination regime that simulated water distribution with residue chlorine. The 7-day DBPs formation potential (DBPsFP) test with chlorine revealed chlorination by-products of phenylalanine including trihalomethanes (THMs), haloacetic acids (HAAs), haloacetonitriles (HANs), and halonitromethanes (HNMs), but not trichloronitromethane (TCNM) which was a significant N-DBP detected during the first 48 h of chlorine contact. The formation of most carbonaceous DBPs (C-DBPs) increased with chlorination time; however N-DBPs and non-chlorinated byproducts of phenylacetonitrile and phenylacetaldehyde reached their highest concentration after 2 h of reaction, and then gradually decreased until below detection after 7 days. The chlorination influencing factors indicated that light enhanced the peak yield of DBPs; the pH value showed different influences associated with corresponding DBPs; and the presence of bromide ions (Br) generated a variety of bromine-containing DBPs. The DBPsFP test with chloramine reduced C-DBPs generation to about 1/3 of the level observed for chlorine disinfection and caused an increase in dichloroacetonitrile. Surveillance of DBPs during drinking water distribution to consumers should consider the varying contact times with disinfectants to accurately profile the types and concentrations of C-DBPs and N-DBPs present in drinking water.
水中溶解的含氮有机物可能含有消毒副产物(DBPs)的前体物,尤其是含氮 DBPs(N-DBPs)。在水源水中,氨基酸作为溶解态含氮有机物普遍存在,并且可以通过饮用水处理工艺传递到出厂水中和配水系统中与消毒剂反应。选择苯丙氨酸(Phe)作为模型氨基酸前体物,研究其在氯消毒模拟管网水中余氯条件下的 DBPs 及其变化。7 天 DBPs 生成潜能(DBPsFP)试验表明,氯消毒生成了苯丙氨酸的氯化副产物,包括三卤甲烷(THMs)、卤乙酸(HAAs)、卤乙腈(HANs)和卤硝基甲烷(HNMs),但在氯接触的前 48 h 内检测到的显著 N-DBP 三氯硝基甲烷(TCNM)并未生成。大多数碳 DBPs(C-DBPs)的生成随氯化时间增加而增加;然而,苯乙腈和苯乙醛的非氯化副产物以及 N-DBPs 在反应 2 h 后达到最高浓度,然后逐渐降低,7 天后检测不到。氯化影响因素表明,光照增强了 DBPs 的峰值生成;pH 值对相应的 DBPs 表现出不同的影响;溴离子(Br)的存在生成了各种含溴 DBPs。氯胺消毒的 DBPsFP 试验使 C-DBPs 的生成量减少到氯消毒时的约 1/3,并导致二氯乙腈的生成增加。在向消费者分配饮用水期间监测 DBPs 时,应考虑与消毒剂的不同接触时间,以准确描述饮用水中存在的 C-DBPs 和 N-DBPs 的类型和浓度。