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脉冲辐射和γ辐射中羟基自由基引发的非草隆降解:动力学与产物分析

Hydroxyl radical-induced degradation of fenuron in pulse and gamma radiolysis: kinetics and product analysis.

作者信息

Kovács Krisztina, Mile Viktoria, Csay Tamás, Takács Erzsébet, Wojnárovits László

机构信息

Institute for Energy Security and Environmental Safety, Centre for Energy Research, Hungarian Academy of Sciences, Budapest, Hungary.

出版信息

Environ Sci Pollut Res Int. 2014 Nov;21(22):12693-700. doi: 10.1007/s11356-014-3197-9. Epub 2014 Jun 26.

DOI:10.1007/s11356-014-3197-9
PMID:24965004
Abstract

Radiolytic reactions of phenylureas were studied in detail with fenuron model compound in dilute aqueous solutions using pulse radiolysis for detection of the intermediates, gamma radiolysis with UV-Vis and HPLC-MS techniques for analysis of the final products. The kinetics of oxidation was followed by COD, TOC and toxicity measurements. During radiolysis of aerated solutions hydroxyl radical ((•)OH), eaq (-), H(•) and O2 (•-)/HO2 (•) reactive intermediates are produced, the degradation of solute takes place practically entirely through (•)OH reactions. Therefore, the product distribution is similar to the distributions reported in other advanced oxidation processes with (•)OH as main reactant. (•)OH mainly reacts with the aromatic ring, forming cyclohexadienyl radical as an intermediate. This radical in pulse radiolysis has a wide absorption band in the 310-390 nm wavelength range with a maximum at 350 nm. Cyclohexadienyl radical reacts with dissolved O2 with a rate coefficient of ∼ 4 × 10(8) mol(-1) dm(3) s(-1) forming peroxy radical. The latter may eliminate HO2 (•) giving phenols or undergoes fragmentation. The one-electron oxidant (•)OH on average induces more than two-electron oxidations. The toxicity first increases with absorbed dose, then decreases. This increase is partly due to phenols formed during the first degradation period.

摘要

使用脉冲辐解检测中间体、利用紫外可见光谱和高效液相色谱-质谱联用技术进行γ辐解以分析最终产物,在稀水溶液中以非草隆为模型化合物对苯基脲的辐射分解反应进行了详细研究。通过化学需氧量(COD)、总有机碳(TOC)和毒性测量来跟踪氧化动力学。在曝气溶液的辐射分解过程中,会产生羟基自由基((•)OH)、水合电子(eaq (-))、氢原子(H(•))和超氧阴离子自由基/O2 (•-)/HO2 (•)等活性中间体,溶质的降解实际上完全通过(•)OH反应进行。因此,产物分布与其他以(•)OH作为主要反应物的高级氧化过程中报道的分布相似。(•)OH主要与芳环反应,形成环己二烯基自由基作为中间体。该自由基在脉冲辐解中在310 - 390 nm波长范围内有宽吸收带,最大吸收波长为350 nm。环己二烯基自由基与溶解的O2反应,反应速率系数约为4 × 10(8) mol(-1) dm(3) s(-1),形成过氧自由基。后者可能消除HO2 (•)生成酚类或发生碎片化。单电子氧化剂(•)OH平均引发超过双电子的氧化反应。毒性首先随吸收剂量增加,然后降低。这种增加部分归因于在第一个降解阶段形成的酚类。

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