Department of Environmental Engineering, College of Environmental Science and Engineering, Peking University, China.
Department of Civil Engineering and Architecture, University of Catania, Viale A. Doria 6, Catania, Italy.
Chemosphere. 2021 Apr;268:129241. doi: 10.1016/j.chemosphere.2020.129241. Epub 2020 Dec 7.
Concentrations of several toxic disinfection by-products (DBP), notably haloacetonitriles (e.g., trichloroacetonitrile, TCAN) and haloketones (e.g., di- and trichloropropanone, DCPN and TCPN, respectively) are affected by chlorination conditions and the inherent instability of these DBPs. In this study, effects of temperature, chlorine dose and reaction time on the formation of TCAN, DCPN and TCPN were interpreted using the approach of differential absorbance spectroscopy. Experimental data obtained for a wide range of water quality conditions demonstrate that in some cases the concentrations of some of the unstable DBPs increased rather than decreased at low temperatures and realistically long contact times. Despite the presence of pronounced changes of the kinetics of generation and degradation of these DBPs at varying temperatures and chlorine doses, their concentrations were strongly correlated with the concurrent changes of spectroscopic properties of DOM quantified via differential absorbance measurements at 272 nm (ΔA). The maximum values of TCAN, DCPN and TCPN concentrations observed for the chlorination of eight different surface waters occur at the relative decreases of absorbance at 272 nm (defined as RΔA) values of ca. 0.32 (±0.03), 0.24 (±0.05), and 0.42 (±0.03), respectively. The activation energies of degradation reactions of unstable DBPs were examined and the results indicate that TCAN and TCPN are caused by their hydrolysis with OH while the degradation of DCPN is mainly caused by halogenation reaction with HOCl. These results in this study may be important for controlling the formation of unstable DBPs and further optimization of drinking water treatment.
几种有毒消毒副产物(DBP)的浓度,特别是卤乙腈(例如三氯乙腈,TCAN)和卤酮(例如二氯丙酮和三氯丙酮,分别为 DCPN 和 TCPN),受氯化条件和这些 DBP 的固有不稳定性的影响。在这项研究中,使用差示吸收光谱法解释了温度、氯剂量和反应时间对 TCAN、DCPN 和 TCPN 形成的影响。在广泛的水质条件下获得的实验数据表明,在某些情况下,一些不稳定 DBP 的浓度在低温和实际长接触时间下增加而不是减少。尽管在不同温度和氯剂量下这些 DBP 的生成和降解动力学发生了明显变化,但它们的浓度与通过 272nm 处的差示吸收测量定量的 DOM 的光谱特性的变化密切相关(ΔA)。在氯化八种不同地表水的过程中观察到 TCAN、DCPN 和 TCPN 浓度的最大值出现在 272nm 处吸光度(定义为 RΔA)相对降低约 0.32(±0.03)、0.24(±0.05)和 0.42(±0.03)时。还检查了不稳定 DBP 降解反应的活化能,结果表明 TCAN 和 TCPN 是由 OH 水解引起的,而 DCPN 的降解主要是由 HOCl 的卤化反应引起的。本研究中的这些结果对于控制不稳定 DBP 的形成和进一步优化饮用水处理可能很重要。