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Degradation of atrazine and structurally related s-triazine herbicides in soils by ferrous-activated persulfate: Kinetics, mechanisms and soil-types effects

机译:用铁 - 活化过硫酸盐在土壤中降解阿特拉津和结构相关的S-三嗪除草剂:动力学,机制和土壤类型效应

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摘要

The occurrence of s-triazine herbicides in soils and groundwaters has been reported globally and remediation of these contaminated sites are essentially imperative, especially at accidental spill sites. Present work investigated the feasibility of using Fe2+ catalyzed persulfate (PS) to effectively degrade s-triazine herbicides (e.g., atrazine (ATZ), terbuthylazine (TEA) and ametryn (AMT)) in soils. The degradation kinetics, mechanisms and soil-types effects were systematically investigated. For arable soil Al, extent of degradation reached 80% for 100 mg kg(-1) ATZ contaminated soil after 600 min (PS/Fe2+ of 16.6 mM/16.6 mM) at 23 degrees C. Increasing PS and Fe2+ dosages could enhance ATZ degradation. Acidic condition was favorable for the degradation of ATZ with Fe2+/PS process and the contribution of SO4 center dot- to the overall degradation of ATZ decreased as initial pH increased. The ethyl group and chloride substituent on molecular structure of ATZ affected its degradation comparing to other two s-triazine herbicides. ATZ degradations in two arable soils and one paddy soil indicated that different soils with various physical-chemical properties, such as soil organic matter, available and total Fe contents, may influence the ATZ degradation. Moreover, a total of five degradation products of ATZ were identified in soil Al by Fe2+/PS process. Three degradation pathways including alkyl chain oxidation, dealkylation and dechlorination-hydroxylation reactions with the underlying oxidation mechanisms were tentatively proposed.
机译:全球据报道,土壤和地下水中的S-三嗪除草剂的发生并对这些受污染部位进行了修复基本上是必不可少的,特别是在意外溢出位点。目前的工作研究了使用Fe2 +催化过硫酸盐(PS)的可行性,以有效降解土壤中的S-三嗪除草剂(例如,亚津(ATZ),Terbuthylazine(AMT))。系统地研究了降解动力学,机制和土壤类型效应。对于耕地Al,在23摄氏度的600分钟(PS / Fe2 + 16.6mm / 16.6mm)下,100mg kg(-1)克斯污染土壤的降解程度达到80%。增加PS和Fe2 +剂量可以增强ATZ降解。酸性条件有利于使用Fe2 + / PS过程的ATZ的降解,并且SO4中心点的贡献随着初始pH增加而降低ATZ的整体降解。乙基和氯化物取代基对ATZ的分子结构影响其降解与其他两个S-三嗪除草剂相比。在两个耕作土壤中的ATZ降解和一个水稻土指出,不同的土壤具有各种物理化学性质,如土壤有机物质,可用和总二氧化碳,可能影响ATZ降解。此外,通过Fe2 + / PS过程,在土壤Al中鉴定了5种ATZ的降解产物。提出了三种降解途径,包括烷基链氧化,诸如与下氧化机制的氧化机制的脱氯 - 羟基化反应。

著录项

  • 来源
    《Chemical engineering journal》 |2018年第2018期|共9页
  • 作者单位

    Nanjing Agr Univ Coll Resources &

    Environm Sci Nanjing 210095 Jiangsu Peoples R China;

    Nanjing Agr Univ Coll Resources &

    Environm Sci Nanjing 210095 Jiangsu Peoples R China;

    Nanjing Agr Univ Coll Resources &

    Environm Sci Nanjing 210095 Jiangsu Peoples R China;

    Nanjing Agr Univ Coll Resources &

    Environm Sci Nanjing 210095 Jiangsu Peoples R China;

    Nanjing Agr Univ Coll Resources &

    Environm Sci Nanjing 210095 Jiangsu Peoples R China;

    Nanjing Agr Univ Coll Resources &

    Environm Sci Nanjing 210095 Jiangsu Peoples R China;

    Sun Yat Sen Univ Sch Environm Sci &

    Engn Guangzhou 510275 Guangdong Peoples R China;

    Nanjing Agr Univ Coll Resources &

    Environm Sci Nanjing 210095 Jiangsu Peoples R China;

  • 收录信息
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类 化学工业;
  • 关键词

    Herbicides; Atrazine; Sulfate radical; Degradation mechanisms; Soil types;

    机译:除草剂;亚得唑嗪;硫酸盐自由基;降解机制;土壤类型;

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