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氯、UV 辐照和 UV/氯工艺对罗硝唑降解的动力学模型和途径。

Kinetic models and pathways of ronidazole degradation by chlorination, UV irradiation and UV/chlorine processes.

机构信息

State Key Laboratory of Pollution Control and Resources Reuse, Key Laboratory of Yangtze Water Environment, Ministry of Education, 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, ROC.

出版信息

Water Res. 2014 Nov 15;65:271-81. doi: 10.1016/j.watres.2014.07.041. Epub 2014 Aug 6.

Abstract

Degradation kinetics and pathways of ronidazole (RNZ) by chlorination (Cl2), UV irradiation and combined UV/chlorine processes were investigated in this paper. The degradation kinetics of RNZ chlorination followed a second-order behavior with the rate constants calculated as (2.13 ± 0.15) × 10(2) M(-2) s(-1), (0.82 ± 0.52) × 10(-2) M(-1) s(-1) and (2.06 ± 0.09) × 10(-1) M(-1) s(-1) for the acid-catalyzed reaction, as well as the reactions of RNZ with HOCl and OCl(-), respectively. Although UV irradiation degraded RNZ more effectively than chlorination did, very low quantum yield of RNZ at 254 nm was obtained as 1.02 × 10(-3) mol E(-1). RNZ could be efficiently degraded and mineralized in the UV/chlorine process due to the generation of hydroxyl radicals. The second-order rate constant between RNZ and hydroxyl radical was determined as (2.92 ± 0.05) × 10(9) M(-1) s(-1). The degradation intermediates of RNZ during the three processes were identified with Ultra Performance Liquid Chromatography - Electrospray Ionization - mass spectrometry and the degradation pathways were then proposed. Moreover, the variation of chloropicrin (TCNM) and chloroform (CF) formation after the three processes were further evaluated. Enhanced formation of CF and TCNM precursors during UV/chlorine process deserves extensive attention in drinking water treatment.

摘要

本文研究了氯(Cl2)、UV 照射和 UV/氯联合工艺对罗硝唑(RNZ)的降解动力学和途径。RNZ 氯化的降解动力学遵循二级行为,计算得到的速率常数分别为(2.13±0.15)×10(2) M(-2) s(-1)、(0.82±0.52)×10(-2) M(-1) s(-1)和(2.06±0.09)×10(-1) M(-1) s(-1),分别为酸催化反应、RNZ 与 HOCl 和 OCl(-)的反应。尽管 UV 照射比氯化更有效地降解 RNZ,但在 254nm 时仅得到非常低的 RNZ 量子产率(1.02×10(-3) mol E(-1))。由于生成了羟基自由基,RNZ 可以在 UV/氯工艺中有效降解和矿化。RNZ 和羟基自由基之间的二级速率常数确定为(2.92±0.05)×10(9) M(-1) s(-1)。用超高效液相色谱-电喷雾电离-质谱鉴定了这三种过程中 RNZ 的降解中间产物,然后提出了降解途径。此外,还进一步评估了三种工艺后三氯硝基甲烷(TCNM)和三氯甲烷(CF)的形成变化。在 UV/氯工艺中 CF 和 TCNM 前体的增强形成值得在饮用水处理中引起广泛关注。

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