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Soil organic matter-hydrogen peroxide dynamics in the treatment of contaminated soils and groundwater using catalyzed H_2O_2 propagations (modified Fenton's reagent)

机译:利用H_2O_2催化扩散(Fenton试剂改性)处理受污染土壤和地下水的土壤有机质-过氧化氢动力学。

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摘要

The interactions between catalyzed H_2O_2 propagations (CHP—i.e. modified Fenton's reagent) and soil organic matter (SOM) during the treatment of contaminated soils and groundwater was studied in a well-characterized surface soil. The fate of two fractions of SOM, particulate organic matter (POM) and nonparticulate organic matter (NPOM), during CHP reactions was evaluated using concentrations of hydrogen peroxide from 0.5 to 3M catalyzed by soluble iron (III), an iron (III)-ethylenediamine tetraacetic acid (EDTA) chelate, or naturally-occurring soil minerals. The destruction of total SOM in CHP systems was directly proportional to the hydrogen peroxide dosage, and was significantly greater at pH 3 than at neutral pH; furthermore, SOM destruction occurred predominantly in the NPOM fraction. At pH 3, SOM did not affect hydrogen peroxide decomposition rates or hydroxyl radical activity in CHP reactions. However, at neutral pH, increasing the mass of SOM decreased the hydrogen peroxide decomposition rate and increased the rate of hydroxyl radical generation in CHP systems. These results show that, while CHP reactions destroy some of the organic carbon pools, SOM does not have a significant effect on the CHP treatment of soils and groundwater.
机译:在表征良好的表层土壤中,研究了在污染土壤和地下水处理过程中催化的H_2O_2传播(CHP,即改良的Fenton试剂)与土壤有机质(SOM)之间的相互作用。在CHP反应过程中,使用可溶性铁(III),铁(III)-催化的0.5至3M的过氧化氢浓度,评估了SOM的两个部分的命运,颗粒有机物(POM)和非颗粒有机物(NPOM)。乙二胺四乙酸(EDTA)螯合物,或天然存在的土壤矿物质。 CHP系统中总SOM的破坏与过氧化氢的剂量成正比,在pH为3时明显大于中性pH。此外,SOM破坏主要发生在NPOM组分中。在pH 3下,SOM不会影响CHP反应中的过氧化氢分解速率或羟基自由基活性。然而,在中性pH下,增加SOM的质量会降低过氧化氢的分解速率,并增加了CHP系统中羟基自由基的生成速率。这些结果表明,尽管CHP反应破坏了一些有机碳库,但是SOM对CHP处理土壤和地下水没有显着影响。

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