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Sonolytic Decomposition of Aqueous Bioxalate in the Presence of Ozone

机译:臭氧存在下生物草酸盐水溶液的声分解

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摘要

Ultrasonic irradiation in the presence of ozone is demonstrated to be effective for the rapid oxidation of oxalic acid, bioxalate, and oxalate (H2C2O4/HC2O4 -/C2O4 2-) in aqueous solution to CO2 and H2O. The degradation rate of bioxalate exposed to “sonozone” (i.e., simultaneous ultrasonication and ozonolysis) was found to be 16-times faster than predicted by the linear addition of ozonolysis and ultrasonic irradiation rates.The hydroxyl radical (OH) is the only oxy-radical produced that can oxidize oxalate on a relevant timescale. Thus, plausible OH production mechanisms are evaluated to explain the observed kinetic synergism of ultrasonication and ozonolysis toward bioxalate decomposition. OH production via decomposition of O3 in the cavitating bubble vapor and via the reaction of O3 and H2O2 are considered, but kinetic estimations and experimental evidence indicate neither to be a sufficient source of OH. A free-radical chain mechanism is proposed in which the HC2O4 - + OH reaction functions as a primary propagation step, while the termination occurs through the O3 + CO2 - reaction via an O-atom transfer mechanism. Kinetic simulations confirm that ozone reacts efficiently with the superoxide (O2 -) ion that is produced by the reaction of O2 and CO2 - to form OH radical, and that the reaction of O3 + CO2 - must be chain terminating. Oxalate is also readily oxidized by “peroxone” treatment (i.e., H2O2 and O3). However, the addition of H2O2 during the course of the sonolytic ozonation of oxalic acid does not appear to increase the observed degradation rate and decreases rates at millimolar levels.
机译:臭氧存在下的超声辐射被证明可有效地将草酸,生物草酸盐和草酸盐(H2C2O4 / HC2O4-/ C2O4 2-)在水溶液中快速氧化为CO2和H2O。发现暴露于“ sonozone”(即同时进行超声处理和臭氧分解)的生物草酸盐的降解速率比通过线性添加臭氧分解和超声辐射速率预测的降解速度快16倍。羟基自由基(OH)是唯一的产生的自由基会在相关时间范围内氧化草酸盐。因此,评估可能的OH产生机理以解释观察到的超声作用和臭氧分解对生物草酸盐分解的动力学协同作用。考虑了通过在空化气泡蒸气中分解O3以及通过O3与H2O2的反应产生OH的方法,但是动力学估算和实验证据表明两者都不是OH的充分来源。提出了一种自由基链机制,其中HC2O4- + OH反应充当主要的传播步骤,而终止反应是通过O-原子转移机制通过O3 + CO2-反应进行的。动力学模拟证实,臭氧与由O2和CO2-形成OH自由基的超氧化物(O2-)离子有效反应,并且O3 + CO2-的反应必须是链终止的。草酸盐也容易通过“过氧化物”处理(即H2O2和O3)氧化。但是,在草酸的声臭氧氧化过程中加入H2O2似乎不会增加观察到的降解速率,也不会降低毫摩尔水平的降解速率。

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