Reductive degradation of chlorinated organophosphate esters by nanoscale zerovalent iron/cetyltrimethylammonium bromide composites: Reactivity, mechanism and new pathways

被引:44
作者
Li, Dan [1 ,3 ,4 ]
Zhong, Yin [1 ]
Zhu, Xifen [1 ,3 ]
Wang, Heli [1 ,3 ]
Yang, Weiqiang [1 ,3 ]
Deng, Yirong [1 ,3 ,5 ]
Huang, Weilin [2 ]
Peng, Ping'an [1 ]
机构
[1] Chinese Acad Sci, Guangdong Prov Key Lab Environm Protect & Resourc, Guangdong Hong Kong Maco Joint Lab Environm Pollu, State Key Lab Organ Geochem,Guangzhou Inst Geoche, Guangzhou 510640, Peoples R China
[2] Rutgers State Univ, Dept Environm Sci, 14 Coll Farm Rd, New Brunswick, NJ 08901 USA
[3] Univ Chinese Acad Sci, Beijing 100049, Peoples R China
[4] Dongguan Univ Technol, Sch Environm & Civil Engn, Dongguan 523808, Peoples R China
[5] Guangdong Prov Acad Environm Sci, Guangdong Key Lab Contaminated Sites Environm Man, Guangzhou 510045, Peoples R China
基金
中国国家自然科学基金;
关键词
TCEP; S-nZVI/CTAB; O; O-di-(2-chloroethyl)O-ethyl phosphate; ethane; hydrophobic adsorption; WASTE-WATER TREATMENT; ZERO-VALENT IRON; FLAME RETARDANTS; POROUS-MEDIA; ELECTROMAGNETIC INDUCTION; TREATMENT PLANTS; KINETICS; TRICHLOROETHYLENE; DECHLORINATION; TRANSFORMATION;
D O I
10.1016/j.watres.2020.116447
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Chlorinated organophosphate esters (Cl-OPEs), e.g., tris(2-chloroethyl) phosphate (TCEP), tris(2-chloro-2-propyl) phosphate (TCPP) and tris(1,3-dichloro-2-propyl) phosphate (TDCPP), are widely used as additive flame retardants in commercial and building products. They have potential persistent organic pollutant properties and are frequently detected in various waters, especially in wastewaters. Nanoscale zerovalent iron (nZVI)-based method is an efficient reductive technology for treating waters polluted by halogenated organic pollutants (HOCs). Cetyltrimethylammonium bromide (CTAB) is a ubiquitous surfactant in wastewaters and can favorably affect the interaction between HOCs and nZVI. However, its effect on the Cl-OPEs removal by nZVI-based materials still remains unknown. Herein, the adsorption and degradation efficiencies of Cl-OPEs by nZVI and sulfidated nZVI (S-nZVI) in the presence or absence of CTAB were quantified based on the decreasing concentrations of Cl-OPEs in reaction systems. Our results showed that TDCPP and TCPP were adsorbed onto the nZVI or S-nZVI surface and subsequently degraded. In contrast, TCEP was just adsorbed onto the particle surface without further degradation. The addition of CTAB significantly enhanced the hydrophobic adsorption between Cl-OPEs and nZVI or S-nZVI, leading to increased degradation of Cl-OPEs (especially TCEP). CTAB adsorption isotherms indicated that S-nZVI had a higher adsorption capacity for CTAB than nZVI. The S-nZVI/CTAB composite exhibited a better performance than nZVI/CTAB composite. When S-nZVI was combined with 100.0 mg L-1 CTAB, 100% of TDCPP, TCPP and TCEP was degraded within 3 hours, 5 and 14 days, respectively. As the concentration of CTAB was increased up to 335.0 mg L-1, TCEP could be completely degraded within 3 days by S-nZVI. Five degradation products of TCEP were identified, of which O,O-di-(2-chloroethyl) O-ethyl phosphate (DCEEP) and ethane were reported for the first time. We propose that TCEP is dechlorinated by nZVI or S-nZVI through the electron attack at the ethyl-chlorine group to form bis(2-chloroethyl) phosphate, DCEEP, chloride, ethene and ethane, representing previously unknown degradation pathways. (C) 2020 Elsevier Ltd. All rights reserved.
引用
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页数:13
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