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首页> 外文期刊>Water Research >Reductive degradation of chlorinated organophosphate esters by nanoscale zerovalent iron/cetyltrimethylammonium bromide composites: Reactivity, mechanism and new pathways
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Reductive degradation of chlorinated organophosphate esters by nanoscale zerovalent iron/cetyltrimethylammonium bromide composites: Reactivity, mechanism and new pathways

机译:纳米级齐价铁/甲苯二甲基溴化物复合材料的氯化有机磷酸酯的还原降解:反应性,机制和新途径

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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.
机译:氯化有机磷酸酯(Cl-oppes),例如Tris(2-氯乙基)磷酸盐(TCEP),Tris(2-氯-2-丙基)磷酸盐(TCPP)和Tris(1,3-二氯-2-丙基)磷酸盐(TDCPP),广泛用作商业和建筑产品中的添加阻燃剂。它们具有潜在的持续有机污染物特性,并且经常在各种水域中检测,特别是在废水中。基于纳米级Zerovalent Iron(NZVI)的方法是一种有效的还原技术,用于治疗被卤化有机污染物(HOC)污染的水。十六烷基三甲基溴化铵(CTAB)是废水中普遍存在的表面活性剂,可以有利地影响HOCS和NZVI之间的相互作用。然而,它对基于NZVI的材料的CL-oppes的影响仍然未知。在此,基于反应体系中的Cl-opes的浓度降低,通过NZVI和硫化NZVI(S-NZVI)在CTAB的存在或不存在中进行的吸附和降解效率。我们的结果表明,TDCPP和TCPP被吸附在NZVI或S-NZVI表面上并随后降解。相反,TCEP恰好被吸附到颗粒表面上而没有进一步降解。 CTAB的添加显着增强了Cl-opes和NZVI或S-NZVI之间的疏水吸附,从而增加了Cl-opes(特别是TCEP)的降解。 CTAB吸附等温线表明,S-NZVI对CTAB的吸附能力较高而不是NZVI。 S-NZVI / CTAB复合材料表现出比NZVI / CTAB复合材料更好的性能。当S-NZVI与100.0mg L-1 CTAB合并时,100%TDCPP,TCPP和TCEP分别在3小时内,5和14天内降解。随着CTAB的浓度增加至335.0mg L-1,TCEP可以通过S-NZVI在3天内完全降解。鉴定了TCEP的五种降解产物,其中首次报道了O,O-DI-(2-氯乙基)O-乙基磷酸乙酯(DCEEP)和乙烷。我们提出通过NZVI或S-NZVI通过在乙基氯基的电子攻击来脱氯,以形成双(2-氯乙基)磷酸酯,DCEEP,氯化物,乙烯和乙烷,代表先前未知的降解途径。 (c)2020 elestvier有限公司保留所有权利。

著录项

  • 来源
    《Water Research 》 |2021年第1期| 116447.1-116447.13| 共13页
  • 作者单位

    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|Univ Chinese Acad Sci Beijing 100049 Peoples R China|Dongguan Univ Technol Sch Environm & Civil Engn Dongguan 523808 Peoples R China;

    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;

    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|Univ Chinese Acad Sci Beijing 100049 Peoples R China;

    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|Univ Chinese Acad Sci Beijing 100049 Peoples R China;

    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|Univ Chinese Acad Sci Beijing 100049 Peoples R China;

    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|Univ Chinese Acad Sci Beijing 100049 Peoples R China|Guangdong Prov Acad Environm Sci Guangdong Key Lab Contaminated Sites Environm Man Guangzhou 510045 Peoples R China;

    Rutgers State Univ Dept Environm Sci 14 Coll Farm Rd New Brunswick NJ 08901 USA;

    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;

  • 收录信息 美国《科学引文索引》(SCI);美国《工程索引》(EI);
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    TCEP; S-nZVI/CTAB; O,O-di-(2-chloroethyl)O-ethyl phosphate; ethane; hydrophobic adsorption;

    机译:TCEP;S-NZVI / CTAB;O;O-DI-(2-氯乙基)O-磷酸乙酯;乙烷;疏水吸附;

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