Department of Civil and Environmental Engineering, University of Waterloo, Waterloo, Ontario, Canada.
Water Res. 2012 Dec 1;46(19):6519-30. doi: 10.1016/j.watres.2012.09.026. Epub 2012 Oct 3.
Second-order reaction rate constants of micropollutants with ozone (k(O3)) and hydroxyl radicals (k(OH)) are essential for evaluating their removal efficiencies from water during ozonation and advanced oxidation processes. Kinetic data are unavailable for many of the emerging micropollutants. Twenty-four micropollutants with very diverse structures and applications including endocrine disrupting compounds, pharmaceuticals, and personal care products were selected, and their k(O3) and k(OH) values were determined using bench-scale reactors (at pH 7 and T = 20 °C). Reactions with molecular ozone are highly selective as indicated by their k(O3) values ranging from 10(-2)-10(7) M(-1) s(-1). The general trend of ozone reactivity can be explained by micropollutant structures in conjunction with the electrophilic nature of ozone reactions. All of the studied compounds are highly reactive with hydroxyl radicals as shown by their high k(OH) values (10(8)-10(10) M(-1) s(-1)) even though they are structurally very diverse. For compounds with a low reactivity toward ozone, hydroxyl radical based treatment such as O(3)/H(2)O(2) or UV/H(2)O(2) is a viable alternative. This study contributed to filling the data gap pertaining kinetic data of organic micropollutants while confirming results reported in the literature where available.
二级反应速率常数是评估臭氧(k(O3))和羟基自由基(k(OH))在臭氧氧化和高级氧化过程中从水中去除污染物效率的重要参数。许多新兴污染物的动力学数据都无法获得。本研究选择了 24 种具有非常不同结构和应用的污染物,包括内分泌干扰物、药物和个人护理产品,并用实验室规模的反应器(在 pH 7 和 T = 20°C 下)确定了它们的 k(O3)和 k(OH)值。与分子臭氧的反应具有高度选择性,这反映在其 k(O3)值范围为 10(-2)-10(7)M(-1)s(-1)。臭氧反应的一般趋势可以通过污染物结构与臭氧反应的亲电性相结合来解释。所有研究的化合物都与羟基自由基高度反应,表现出高 k(OH)值(10(8)-10(10)M(-1)s(-1)),尽管它们的结构非常多样化。对于对臭氧反应性低的化合物,基于羟基自由基的处理方法,如 O(3)/H(2)O(2)或 UV/H(2)O(2),是一种可行的替代方法。本研究有助于填补有关有机污染物动力学数据的空白,同时在可用的情况下确认了文献中报告的结果。