State Key Laboratory of Pollution Control and Resource Reuse, Institute of Disinfection By-product Control in Water Treatment, College of Environmental Science and Engineering, Tongji University, Shanghai 200092, PR China.
Department of Safety, Health and Environmental Engineering, National Kaohsiung First University of Science and Technology, Kaohsiung 824, Taiwan, R.O.C.
Sci Total Environ. 2018 Feb 15;615:38-46. doi: 10.1016/j.scitotenv.2017.09.141. Epub 2017 Oct 17.
Acrylamide is a monomer of polyacrylamide, which is widely used in the water treatment process as a flocculant. The degradation kinetics and formation of disinfection by-products (DBPs) during acrylamide chlorination were investigated in this study. The reaction between chlorine and acrylamide followed a pseudo-first-order kinetics. A kinetic model regarding acrylamide chlorination was established and the rate constants of each predominant elementary reaction (i.e., the base-catalyzed reaction of acrylamide with ClO as well as the reactions of acrylamide with HOCl and ClO) were calculated as 7.89×10Mh, 7.72×10Mh, and 1.65×10Mh, respectively. The presence of Br in water led to the formation of HOBr and accelerated the rate of acrylamide degradation by chlorine. The reaction rate constant of acrylamide with HOBr was calculated as 1.33×10Mh. The degradation pathways of acrylamide chlorination were proposed according to the intermediates identified using ultra-performance liquid chromatography and electrospray ionization-quadrupole time-of-flight mass spectrometry (UPLC-Q-TOF/MS). Five chlorinated DBPs including chloroform (CF), dichloroacetonitrile (DCAN), trichloroacetonitrile (TCAN), dichloroacetamide (DCAcAm), and trichloroacetamide (TCAcAm) were identified during acrylamide chlorination. The formation of CF, DCAN, DCAcAm, and TCAcAm kept increasing, while that of TCAN increased and then decreased with increasing reaction time. As the chlorine dosage increased from 0.75 to 4.5mM, DCAN became the dominant DBP. Large amounts of CF, DCAN, and TCAN were formed at basic pHs. The hydrolysis of DCAN and TCAN led to the formation of DCAcAm and TCAcAm, respectively. The results of this study elucidated that acrylamide can be a precursor for the formation of haloacetonitriles (HANs) and haloacetamides (HAcAms) during drinking water treatment.
丙烯酰胺是聚丙烯酰胺的单体,广泛用作水处理过程中的絮凝剂。本研究考察了丙烯酰胺氯化过程中的降解动力学和消毒副产物(DBP)的形成。氯与丙烯酰胺的反应遵循伪一级动力学。建立了丙烯酰胺氯化动力学模型,并计算了各主要基元反应(即丙烯酰胺与 ClO 的碱催化反应以及丙烯酰胺与 HOCl 和 ClO 的反应)的速率常数分别为 7.89×10Mh、7.72×10Mh 和 1.65×10Mh。水中 Br 的存在会形成 HOBr 并加速氯对丙烯酰胺的降解速率。计算得到丙烯酰胺与 HOBr 的反应速率常数为 1.33×10Mh。根据超高效液相色谱和电喷雾电离-四极杆飞行时间质谱(UPLC-Q-TOF/MS)鉴定的中间体,提出了丙烯酰胺氯化的降解途径。在丙烯酰胺氯化过程中鉴定出五种氯代 DBPs,包括氯仿(CF)、二氯乙腈(DCAN)、三氯乙腈(TCAN)、二氯乙酰胺(DCAcAm)和三氯乙酰胺(TCAcAm)。随着反应时间的增加,CF、DCAN、DCAcAm 和 TCAcAm 的形成不断增加,而 TCAN 的形成则先增加后减少。随着氯剂量从 0.75 增加到 4.5mM,DCAN 成为主要的 DBP。在碱性 pH 值下,会形成大量的 CF、DCAN 和 TCAN。DCAN 和 TCAN 的水解分别导致 DCAcAm 和 TCAcAm 的形成。本研究结果表明,在饮用水处理过程中,丙烯酰胺可能是卤乙腈(HANs)和卤乙酰胺(HAcAms)形成的前体。