Effect of chlorination on the characteristics of effluent organic matter and the phototransformation of sulfamethoxazole in secondary wastewater

被引:17
作者
Li, Wei [1 ,2 ]
Ding, Chun [1 ]
Korshin, Gregory [3 ]
Li, Jiping [1 ]
Cheng, Hu [1 ]
机构
[1] Nanjing Forestry Univ, Coll Biol & Environm, Coinnovat Ctr Sustainable Forestry Southern China, Longpan Rd 159, Nanjing 210037, Peoples R China
[2] Natl Positioning Observat Stn Hung Tse Lake Wetla, Hongze 223100, Jiangsu, Peoples R China
[3] Univ Washington, Dept Civil & Environm Engn, Box 352700, Seattle, WA 98195 USA
基金
中国国家自然科学基金;
关键词
Effluent organic matter; Chlorination; Photochemical activity; Sulfamethoxazole; Three-dimensional excitation emission matrix (3D-EEM); OXYGEN SPECIES ROS; TRANSFORMATION PRODUCTS; SULFONAMIDE ANTIBIOTICS; AQUATIC ENVIRONMENT; INDIRECT PHOTOLYSIS; PHOTODEGRADATION; MICROPOLLUTANTS; OXIDATION; EMISSION; INSIGHTS;
D O I
10.1016/j.chemosphere.2021.133193
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Chlorination is the most common disinfection technology used to treat wastewater effluent discharged into receiving aquatic environments. Effluent organic matter (EfOM) abundant in wastewater is a well-known photosensitizer and it greatly affects phototransformation of antibiotics in water. However, effects of chlorination on the characteristics and photochemical properties of EfOM have not been studied in sufficient detail. This paper investigated effects of chlorination on the characteristics of EfOM, and its impact on the photo transformation of sulfamethoxazole (SMX). Correlations between the EfOM characteristics and steady-state concentrations of reactive intermediates (RI) formed in the system were established. Chlorination was shown to preferentially remove the aromatic protein-like substances in EfOM, and the incorporation of chlorine into followed by the cleavage of the aromatic rings in EfOM molecules led to the formation of low molecular aliphatic organic matter. Both unaltered and chlorinated EfOM promoted the photodegradation of SMX whose rate constant in the wastewater was 1.32-1.65 times higher than that in pH 8 phosphate buffer. However, the rate of SMX photodegradation decreased at higher chlorination concentrations. The photodegradation of SMX was found to proceed through direct photolysis and oxidation by the RIs generated from EfOM and the self-sensitization of SMX. The steady-state concentrations of center dot OH, O-1(2) and 3EfOM* were 2.15-5.50 x 10-16, 0.42-1.51 x 10(-13), and 2.54-5.82 x 10(-14) M in unaltered and chlorinated wastewater. The steady-state concentrations of center dot OH were well correlated with the removal of the fluorescence regional integration (Delta FRI) for humic-like and soluble microbial products (SMPs), while the photodegradation rate constant of SMX and the steady-state concentration of O-1(2) and 3EfOM* showed good correlations with AFRI for tryptophan and fulvic-like substances. Six transformation products (TPs) of SMX were identified. These findings provide new insights into the photochemical properties of chlorinated EfOM in the aquatic environments and its roles in the degradation of antibiotics and other trace-level pharmaceuticals.
引用
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页数:9
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