Impact of ozonation on disinfection byproducts formation from phenylalanine during chlorination

被引:2
作者
Huang, Sinong [1 ]
Liu, Hongwei [1 ]
Wei, Kunming [1 ]
Zhang, Liang [1 ]
Ma, Xiaoyan [1 ]
Li, Qingsong [2 ]
Li, Xueyan [3 ]
Dietrich, Andrea M. [4 ]
机构
[1] Zhejiang Univ Technol, Coll Civil Engn, Zhejiang Key Lab Civil Engn Struct & Disaster Prev, Hangzhou 310023, Peoples R China
[2] Xiamen Univ Technol, Water Resources & Environm Inst, Xiamen 361005, Peoples R China
[3] Suzhou Univ Sci & Technol, Sch Environm Sci & Engn, Suzhou 215009, Peoples R China
[4] Virginia Polytech Inst & State Univ, Civil & Environm Engn, Blacksburg, VA 24061 USA
来源
JOURNAL OF ENVIRONMENTAL SCIENCES | 2024年 / 144卷
基金
中国国家自然科学基金;
关键词
Ozone; Amino acids; Chlorination; Disinfection by-products; DRINKING-WATER; AMINO-ACIDS; ORGANIC-MATTER; TRIHALOMETHANE FORMATION; CELL CYTOTOXICITY; PRE-OZONATION; HUMIC-ACID; PRECURSORS; BROMIDE; OZONE;
D O I
10.1016/j.jes.2023.08.030
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
As a strong oxidizing agent, ozone is used in some water treatment facilities for disinfection, taste and odor control, and removal of organic micropollutants. Phenylalanine (Phe) was used as the target amino acid to comprehensively investigate variability of disinfection byproducts (DBPs) formation during chlorine disinfection and residual chlorine conditions subsequent to ozonation. The results showed that subsequent to ozonation, the typical regulated and unregulated DBPs formation potential (DBPsFP), including trichloromethane (TCM), dichloroacetonitrile (DCAN), chloral hydrate (CH), dichloroacetic acid (DCAA), trichloroacetic acid (TCAA), and trichloroacetamide (TCAcAm) increased substantially, by 2.4, 3.3, 5.6, 1.2, 2.5, and 6.0 times, respectively, compared with only chlorination. Ozonation also significantly increased the DBPs yield under a 2 day simulated residual chlorine condition that mimicked the water distribution system. DBPs formations followed pseudo first order kinetics. The formation rates of DBPs in the first 6 hr were higher for TCM (0.214 hr(-1) ), DCAN (0.244 hr(-1) ), CH (0.105 hr(-1) ), TCAcAm (0.234 hr(-1) ), DCAA (0.375 hr(-1) ) and TCAA (0.190 hr(-1) ) than thereafter. The peak DBPsFP of TCM, DCAN, CH, TCAcAm, DCAA, and TCAA were obtained when that ozonation time was set at 5-15 min. Ozonation times > 30 min increased the mineralization of Phe and decreased the formation of DBPs upon chlorination. Increasing bromine ion (Br-) concentration increased production of bromineDBPs and decreased chlorine-DBPs formation by 59.3%-92.2% . Higher ozone dosages and slight alkaline favored to reduce DBP formation and cytotoxicity. The ozonation conditions should be optimized for all application purposes including DBPs reduction. (c) 2024 The Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences. Published by Elsevier B.V.
引用
收藏
页码:199 / 211
页数:13
相关论文
共 71 条
[1]   Kinetics and mechanisms of formation of bromophenols during drinking water chlorination: Assessment of taste and odor development [J].
Acero, JL ;
Piriou, P ;
von Gunten, U .
WATER RESEARCH, 2005, 39 (13) :2979-2993
[2]   Ultraviolet absorbance monitoring for removal of DBP-precursor in waters with variable quality: Enhanced coagulation revisited [J].
Beauchamp, Nicolas ;
Bouchard, Christian ;
Dorea, Caetano ;
Rodriguez, Manuel .
SCIENCE OF THE TOTAL ENVIRONMENT, 2020, 717
[3]   Precursors of nitrogenous disinfection by-products in drinking water-A critical review and analysis [J].
Bond, Tom ;
Templeton, Michael R. ;
Graham, Nigel .
JOURNAL OF HAZARDOUS MATERIALS, 2012, 235 :1-16
[4]   Formation of odorous by-products during chlorination of major amino acids in East Taihu Lake: Impacts of UV, UV/PS and UV/H2O2 pre-treatments [J].
Cai, Luyang ;
Li, Lei ;
Yu, Shuili ;
Guo, Jingxuan ;
Kuppers, Stephan ;
Dong, Lei .
WATER RESEARCH, 2019, 162 :427-436
[5]   Formation of halogenated C-, N-DBPs from chlor(am)ination and UV irradiation of tyrosine in drinking water [J].
Chu, Wenhai ;
Gao, Naiyun ;
Krasner, Stuart W. ;
Templeton, Michael R. ;
Yin, Daqiang .
ENVIRONMENTAL POLLUTION, 2012, 161 :8-14
[6]   Effect of bromide ion on haloacetic acid speciation resulting from chlorination and chloramination of aquatic humic substances [J].
Cowman, GA ;
Singer, PC .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1996, 30 (01) :16-24
[7]   Hydroxyl radical ozone ratios during ozonation processes.: I-The Rct concept [J].
Elovitz, MS ;
von Gunten, U .
OZONE-SCIENCE & ENGINEERING, 1999, 21 (03) :239-260
[8]   Factors governing odorous aldehyde formation as disinfection by-products in drinking water [J].
Froese, KL ;
Wolanski, A ;
Hrudey, SE .
WATER RESEARCH, 1999, 33 (06) :1355-1364
[9]   Removal of disinfection byproduct (DBP) precursors in water by two-stage biofiltration treatment [J].
Fu, Jie ;
Lee, Wan-Ning ;
Coleman, Clark ;
Nowack, Kirk ;
Carter, Jason ;
Huang, Ching-Hua .
WATER RESEARCH, 2017, 123 :224-235
[10]   Effect of UV wavelength on humic acid degradation and disinfection by-product formation during the UV/chlorine process [J].
Gao, Ze-Chen ;
Lin, Yi-Li ;
Xu, Bin ;
Xia, Ying ;
Hu, Chen-Yan ;
Zhang, Tian-Yang ;
Cao, Tong-Cheng ;
Chu, Wen-Hai ;
Gao, Nai-Yun .
WATER RESEARCH, 2019, 154 :199-209