首页> 外文期刊>Journal of Environmental Science and Health. A >AQUEOUS DEGRADATION OF VOCs IN THE OZONE COMBINED WITH HYDROGEN PEROXIDE OR UV RADIATION PROCESSES 1. EXPERIMENTAL RESULTS
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AQUEOUS DEGRADATION OF VOCs IN THE OZONE COMBINED WITH HYDROGEN PEROXIDE OR UV RADIATION PROCESSES 1. EXPERIMENTAL RESULTS

机译:与过氧化氢或紫外线辐射过程相结合的臭氧中VOC的水溶液降解1.实验结果

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Trichlorothane, TCA, and trichloroethypene, TCE, have been taken as model compounds ot study the elimination of volatile organochlorine compounds present in surface waters with ozone combined with hydrogen peroxide or UV radiation. The effect of gas flow rate, water type (surface and ultrapure water), hydrogen peroxide concentration and oxidation type (ozonation alone, UV radiation alone and combined ozonation with hydrogen peroxide or UV radiation) have been observed on the elimination of VOCs. Reactions of ozone in this system develop in the slow kinetic regime of absorption except when a concentration of hydrogen peroxide higher then a 10~-3 M is applied. Rates of VOC elimination follow pseudo first order kinetics and can be represented by the contribution of four terms due to volatility, hydroxyl radical oxidation, direct reaction with ozone and direct photolysis, the latter two in the case of TCE. Because of the elevated vapor pressure, volatility is the only way of elimination of TCA when treated at 20 Lh~-1 in spite of the presence of ozone and hydrogen peroxide. At low gas flow rate, 2.5 Lh~-1, volatility of TCA still represents 85/100 of elimination rate. For TCE, hydroxyl radical oxidation can be, in some cases, the main pathway of oxidation followed by volatility. In all cases, hydroxyl radical oxidation contribution is increased when the oxidation is carried out in ultrapure water. Combination of ozone with hydrogen peroxide or UV radiation leads to oxidation rates two three times those due to volatility, depending on the gas flow rate applied and type of VOC.
机译:三氯乙烷(TCA)和三氯乙烯(TCE)已被用作模型化合物,以研究臭氧与过氧化氢或紫外线辐射相结合消除地表水中存在的挥发性有机氯化合物。在消除VOC方面,已观察到气体流速,水类型(地表水和超纯水),过氧化氢浓度和氧化类型(单独的臭氧化,单独的UV辐射以及与过氧化氢或UV辐射的合并臭氧化)的影响。在该系统中,臭氧的反应以缓慢的吸收动力学机制发展,除非所用的过氧化氢浓度高于10〜-3M。 VOC的消除速率遵循伪一级动力学,可以通过挥发性,羟基自由基氧化,与臭氧的直接反应和直接光解这四个术语的贡献来表示,在TCE中,后两个因子可以表示。由于蒸气压升高,尽管存在臭氧和过氧化氢,但在20 Lh〜-1处理时,挥发性是消除TCA的唯一方法。在低气体流速(2.5 Lh〜-1)下,三氯乙酸的挥发度仍代表清除率的85/100。对于TCE,在某些情况下,羟基自由基氧化可能是氧化然后挥发的主要途径。在所有情况下,当在超纯水中进行氧化时,羟基自由基的氧化作用都会增加。臭氧与过氧化氢或紫外线辐射的结合导致的氧化速率是挥发性的两倍,这取决于所施加的气体流速和VOC的类型,是挥发性的三倍。

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