Photodegradation of bromochloronitromethane under UV irradiation

被引:0
|
作者
Dai W. [1 ]
Deng L. [1 ]
Xu Y. [1 ]
Wen L. [1 ]
机构
[1] School of Civil Engineering, Southeast University, Nanjing
来源
Deng, Lin (dlwhu@163.com) | 1600年 / Southeast University卷 / 50期
关键词
Bromochloronitromethane(BCNM); Kinetics; Photodegradation; Ultraviolet(UV) irradiation;
D O I
10.3969/j.issn.1001-0505.2020.04.021
中图分类号
学科分类号
摘要
To study the photodegradation of bromochloronitromethane (BCNM) under ultraviolet (UV) irradiation, the effects of UV light intensity, initial concentration, pH, free chlorine and bromide ions on the photodegradation of BCNM were investigated. The results show that the photodegradation of BCNM increases with the increase in UV light intensity and pH, but decreases with the increase in initial concentration. When free chlorine and bromide ions are added, the photodegradation of BCNM increases with the increase in the concentration of added substances. Besides, when free chlorine is added, BCNM is degraded together with the formation of bromodichloronitromethane (BDCNM), dichloronitromethane (DCNM), chloromethane (CNM), trichloronitromethane (TCNM) and bromonitromethane (BNM). The production increases initially and then decreases with the reaction time and the peak increases with the increase in free chlorine concentration. The photodegradation of BCNM under UV irradiation follows the quasi-first-order reaction kinetics equation when the concentration of BCNM is in the range from 0 to 600 μg/L.This study can help control the production of BCNM during the disinfection of drinking water and wastewater. © 2020, Editorial Department of Journal of Southeast University. All right reserved.
引用
下载
收藏
页码:760 / 766
页数:6
相关论文
共 26 条
  • [1] Hu J, Song H, Addison J W, Et al., Halonitromethane formation potentials in drinking waters, Water Research, 44, 1, pp. 105-114, (2010)
  • [2] pp. 4-31, (2018)
  • [3] Marsa A, Cortes C, Teixido E, Et al., In vitro studies on the tumorigenic potential of the halonitromethanes trichloronitromethane and bromonitromethane, Toxicology in Vitro, 45, pp. 72-80, (2017)
  • [4] Yin J B, Wu B, Zhang X X, Et al., Comparative toxicity of chloro- and bromo-nitromethanes in mice based on a metabolomic method, Chemosphere, 185, pp. 20-28, (2017)
  • [5] Dong H Y, Qiang Z M, Lian J F, Et al., Degradation of nitro-based pharmaceuticals by UV photolysis: Kinetics and simultaneous reduction on halonitromethanes formation potential, Water Research, 119, pp. 83-90, (2017)
  • [6] Woo Y T, Lai D, McLain J L, Et al., Use of mechanism-based structure-activity relationships analysis in carcinogenic potential ranking for drinking water disinfection by-products, Environmental Health Perspectives, 110, pp. 75-87, (2002)
  • [7] Dong H Y, Qiang Z M, Hu J, Et al., Degradation of chloramphenicol by UV/chlorine treatment: Kinetics, mechanism and enhanced formation of halonitromethanes, Water Research, 121, pp. 178-185, (2017)
  • [8] Bond T, Templeton M R, Mokhtar Kamal N H, Et al., Nitrogenous disinfection byproducts in English drinking water supply systems: Occurrence, bromine substitution and correlation analysis, Water Research, 85, pp. 85-94, (2015)
  • [9] Yang L Y, Chen X M, She Q H, Et al., Regulation, formation, exposure, and treatment of disinfection by-products (DBPs) in swimming pool waters: A critical review, Environment International, 121, pp. 1039-1057, (2018)
  • [10] Krasner S W, Westerhoff P, Chen B Y, Et al., Occurrence of disinfection byproducts in United States wastewater treatment plant effluents, Environmental Science & Technology, 43, 21, pp. 8320-8325, (2009)