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臭氧氧化降解水中两种农药的动力学和机理。

Kinetics and mechanism of the degradation of two pesticides in aqueous solutions by ozonation.

机构信息

Department of Civil and Environmental Engineering, University of Alberta, Edmonton, Canada.

出版信息

Chemosphere. 2010 Jan;78(5):557-62. doi: 10.1016/j.chemosphere.2009.11.014. Epub 2009 Dec 22.

Abstract

This study evaluated the reaction kinetics and degradation mechanism of the pesticides bromoxynil and trifluralin during conventional ozonation. The second-order rate constants for the direct molecular ozone and hydroxyl radical reactions with bromoxynil and trifluralin were determined using a rapid-scan stopped-flow spectrophotometry, competition kinetics, and an organic substrate monitoring method. High reactivity toward ozone and hydroxyl radicals was observed for bromoxynil and trifluralin. The second-order rate constants for the reaction with ozone were about 10(2)M(-1)s(-1). The values of the second-order rate constants for the reaction between hydroxyl radicals and bromoxynil and trifluralin in ultrapure water at 20 degrees C were estimated to be around 8.4x10(9) and 7.5x10(9)M(-1)s(-1), respectively. The identification of oxidation by-products generated during ozonation was also addressed. It was found that hydroxylation and debromination were the primary pathways for the bromoxynil degradation, whereas hydroxylation and dealkylation were found to be the major mechanisms for trifluralin oxidation.

摘要

本研究评估了常规臭氧化过程中农药溴苯腈和氟乐灵的反应动力学和降解机制。使用快速扫描停流分光光度法、竞争动力学和有机底物监测方法,确定了溴苯腈和氟乐灵与直接分子臭氧和羟基自由基的二级反应速率常数。溴苯腈和氟乐灵对臭氧和羟基自由基具有很高的反应活性。与臭氧的反应的二级速率常数约为 10(2)M(-1)s(-1)。在 20°C 的超纯水中,羟基自由基与溴苯腈和氟乐灵之间的二级速率常数估计分别约为 8.4x10(9)和 7.5x10(9)M(-1)s(-1)。还解决了臭氧化过程中生成的氧化副产物的鉴定问题。研究发现,羟基化和脱溴是溴苯腈降解的主要途径,而羟基化和脱烷基化则是氟乐灵氧化的主要机制。

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