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Degradation of Perfluorooctanoic Acid (PFOA) by Reactive Species Generated through Catalyzed Hydrogen Peroxide Propagation Reactions(ABSTRACT)

机译:通过催化过氧化氢传播反应产生的反应物种通过催化物质降解全氟辛酸(PFOA)(摘要)

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摘要

Perfluorinated compounds (PFCs) are emerging contaminants of increasing environmental and public health concern because of their persistence and bioaccumulation. Perfluorooctanoic acid (PFOA) is a typical PFC used by industry in surfactants, fire retardants, high temperature lubricants, and as a polymer additive for the production of Teflon. The diverse industrial applications of PFCs are related to the unique physicochemical properties of the strong carbon-fluorine (C-F) bond, which creates a thermally stable compound. Numerous treatment technologies including photocatalytic oxidation, photolysis, photochemical reduction, sonochemical pyrolysis, and granular activated carbon filtration have been investigated for PFOA degradation, but none are highly effective. Hydroxyl radical (OH.), which is usually effective in oxidizing saturated and unsaturated carbon bonds in organic pollutants, is ineffective for degrading PFOA (k_(OH·+PFOA) ≤ 10~5 L.mol~(-1)·s~(-1)). Modified Fenton's reagent or catalyzed H2O2 propagation is based on the catalyzed decomposition of hydrogen peroxide by soluble iron, iron chelates, or iron minerals to generate the strong oxidant OH·, as well as other reactive species such as perhydroxyl radical (HO_2~-), superoxide radical anion (O_2~(-·)), and hydroperoxide anion (HO_2~-) through propagation reactions. Some of these species function as reductants and nucleophiles (O_2~(-.) and HO_2~-), and may have the potential to degrade PFCs. The purpose of this research was to investigate the effectiveness of CHP for degrading PFOA, and if effective, the reactive oxygen species responsible for its degradation.
机译:全氟化合物(PFC类)的出现,因为其持久性和生物累积增加的环境和公众健康问题的污染物。全氟辛酸(PFOA)是在表面活性剂,阻燃剂,高温润滑剂中使用由工业的典型PFC,并作为用于生产聚四氟乙烯的聚合物添加剂。 PFCs的不同的工业应用都与强碳 - 氟(C-F)键,它创建了一个热稳定的化合物的独特的物理化学性质。许多治疗技术,包括光催化氧化,光解,光化学还原,声化学热解,和颗粒状活性炭过滤已被研究用于PFOA降解,但没有一个是非常有效的。羟基自由基(OH),它通常是在氧化饱和的和中的有机污染物的不饱和碳键,是无效的降解PFOA(K_(OH·+ PFOA有效)≤10〜5 L.mol〜(-1)·S〜 (-1))。改性Fenton试剂或催化H 2 O 2的传播是基于由可溶性铁,铁螯合物,或铁矿物的过氧化氢的催化分解以产生强氧化剂OH·,以及其它反应性物质,如过羟基自由基(HO_2〜 - ),通过增长反应超氧阴离子自由基阴离子(O_2〜( - - ·)),以及氢过氧化物阴离子(HO_2〜)。有些物种作为还原剂和亲核试剂(O_2〜( - )和HO_2〜 - ),并可能有降解的PFC的潜力。这项研究的目的是调查CHP的有效性降低PFOA,如果有效,负责其降解的活性氧。

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