Degradation of Triclosan in soils by thermally activated persulfate under conditions representative of in situ chemical oxidation (ISCO)

被引:63
|
作者
Chen, Liwei [1 ]
Hu, Xiaoxin [1 ]
Cai, Tianming [1 ]
Yang, Ying [1 ]
Zhao, Rudong [2 ]
Liu, Chao [1 ]
Li, Anyun [3 ]
Jiang, Canlan [1 ]
机构
[1] Nanjing Agr Univ, Coll Resources & Environm Sci, Nanjing 210095, Jiangsu, Peoples R China
[2] Chinese Acad Sci, Key Lab Aquat Bot & Watershed Ecol, Wuhan Bot Garden, Wuhan 430074, Hubei, Peoples R China
[3] Changjiang Water Resources Commiss, Network & Informat Ctr, Wuhan 430010, Hubei, Peoples R China
基金
中国国家自然科学基金;
关键词
Antimicrobial agents; Triclosan; Soil remediation; Sulfate radical; Transformation pathways; WASTE-WATER TREATMENT; ORGANIC-MATTER; RATE CONSTANTS; CONTAMINATED SOIL; MECHANISM; TRICLOCARBAN; KINETICS; GROUNDWATER; REMEDIATION; POLLUTANT;
D O I
10.1016/j.cej.2019.03.084
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 widely used antimicrobial agent, Triclosan (TCS) may potentially enter the environment, thus invoking significant environmental concerns due to its high toxicity to organisms. The present study demonstrated that a thermally activated persulfate (PS) oxidation process could effectively degrade the TCS in various arable topsoils. Eighty percent of the TCS at 50 mg kg(-1) in Zhe Jiang (ZJ) soil could be degraded after a 360 min reaction in the presence of 18.8 mM of PS. Increased PS concentrations significantly increased the efficiency of the degradation. Elevated temperatures were favorable for TCS degradation, and the apparent activation energy E-alpha was determined to be 74.3 kJ mol(-1). The oxidation efficiency gradually decreased with the increase of the pH from 3 to 11. An electron paramagnetic resonance (EPR) experiment and radical scavenging test confirmed that both OH center dot and SO4 center dot- existed during oxidation, and SO4 center dot- was the dominant radical species. The degradation efficiency of TCS was higher than that of Triclocarban (TCC), another widely used antimicrobial agent, which might be attributed to the electro-donating phenolic (-OH) and ether (-O-) groups in the molecular structure of TCS. The degradation of TCS in three arable topsoils indicated that the soil organic matter played a dominant role in TCS degradation. In ZJ soil, after the oxidation process, the soil's SOM was decreased by 14%, and the breakdown of large soil aggregates into smaller ones was found. Moreover, two degradation products of TCS were identified, e.g., penta-hydroxylated and hexa-hydroxylated TCS, which may be less toxic. The degradation was induced by phenol ring hydroxylation, and the underlying oxidation mechanisms are given.
引用
收藏
页码:344 / 352
页数:9
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