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Model System Study of Environmentally Persistent Free Radicals Formation in a Semiconducting Polymer Modified Copper Clay System at Ambient Temperature

机译:半导电聚合物改性铜粘土体系中环境持久性自由基形成的模型系统研究

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摘要

This paper systematically investigates how environmentally persistent free radicals (EPFRs) are formed in a phenol contaminated model soil. Poly-p-phenylene (PPP) modified and copper-loaded montmorillonite (MMT) clays were developed and used as models of soil organic matter and the clay mineral component, respectively, with phenol being employed as a precursor pollutant. The polymer modification of the clays was carried out via surface-confined Kumada catalyst-transfer chain-growth polymerization. The presence and location of the polymer were confirmed by a combination of thermogravimetric analysis (TGA), Raman spectroscopy, and X-ray diffraction data. EPFRs were formed by the Cu(II)-clay (Cu(II)CaMMT) and poly-p-phenylene-Cu(II)clay (PPP-Cu(II)CaMMT) composite systems under environmentally relevant conditions. The g-factor and concentration of EPFRs formed by the Cu(II)CaMMT and PPP-Cu(II)CaMMT systems were found to be 2.0034 and 1.22 × 1017 spins/g and 2.0033 and 1.58 × 1017spins/g, respectively. These g-factors are consistent with the formation of phenoxyl radicals. Extended X-Ray absorption fine structure (EXAFS) analysis shows that there are distinct differences in the local stuctures of the phenoxyl radicals associated with only the Cu(II) redox centers and those formed in the presences of the PPP polymer. X-ray absorption near edge spectroscopy (XANES) results provided evidence for the reduction of Cu(II) to Cu(I) in the EPFR forming process. The 1/e lifetimes of the formed EPFRs revealed a decay time of ~20 h for the Cu(II)CaMMT system and a two-step decay pattern for the PPP-Cu(II)CaMMT system with decay times of ~13.5 h and ~55.6 h. Finally, the generation of reactive oxygen species (hydroxyl radical; OH) by these clay systems was also investigated, with higher concentrations of OH detected for the phenol-dosed Cu(II)CaMMT and PPP-Cu(II)CaMMT systems, compared to the non-EPFR containing undosed PPP-Cu(II)CaMMT system.
机译:本文系统地研究了在受苯酚污染的模型土壤中如何形成环境持久性自由基(EPFR)。开发了聚对苯撑(PPP)改性和铜负载蒙脱土(MMT)粘土,分别用作土壤有机质和粘土矿物成分的模型,苯酚被用作前体污染物。粘土的聚合物改性是通过表面受限的Kumada催化剂转移链增长聚合进行的。聚合物的存在和位置通过热重分析(TGA),拉曼光谱和X射线衍射数据的组合来确认。 EPFR由Cu(II)-粘土(Cu(II)CaMMT)和聚对亚苯基-Cu(II)粘土(PPP-Cu(II)CaMMT)复合体系在与环境相关的条件下形成。 Cu(II)CaMMT和PPP-Cu(II)CaMMT系统形成的EPFR的g因子和浓度分别为2.0034和1.22×10 17 spins / g和2.0033和1.58× 10 17 spins / g。这些g因子与苯氧基自由基的形成是一致的。扩展的X射线吸收精细结构(EXAFS)分析表明,仅与Cu(II)氧化还原中心有关的苯氧基自由基和在PPP聚合物存在下形成的苯氧基自由基的局部结构存在明显差异。 X射线吸收近边缘光谱法(XANES)的结果提供了在EPFR形成过程中将Cu(II)还原为Cu(I)的证据。所形成的EPFR的1 / e寿命显示Cu(II)CaMMT系统的衰减时间为〜20 h,而PPP-Cu(II)CaMMT系统的衰减时间为〜13.5 h的两步衰减模式为〜55.6小时最后,还研究了由这些粘土体系生成的活性氧(羟基自由基; OH),并发现了较高浓度的苯酚铜中的 OH (II)CaMMT和PPP-Cu(II)CaMMT系统,与不包含未使用PPP-Cu(II)CaMMT系统的非EPFR相比。

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