State Key Laboratory of Urban Water Resource and Environment, School of Municipal & Environmental Engineering, Harbin Institute of Technology, Harbin 150090, China.
Chemosphere. 2012 Jun;87(10):1134-40. doi: 10.1016/j.chemosphere.2012.02.007. Epub 2012 Mar 3.
The rate constants of sulfamethoxazole (SMX) degradation by ozonation and UV(254) radiation were investigated under various parameters including influent ozone gas concentration, initial SMX concentration, UV light intensity, ionic strength, water quality in terms of varying anions (bicarbonate, sulfate and nitrate), humic acid (HA) and pH. The results indicated that the removal of SMX by ozonation and UV(254) radiation fitted well to a pseudo first-order kinetic model and the rate constants were in the range of (0.9-9.8)×10(-3) and (1.7-18.9)×10(-3) s(-1), respectively. The second-order rate constants of SMX with ozone (ko(3)), under varying operational parameters, were also determined and varied in the range of (0.60-3.38)±0.13×10(5)M(-1) s(-1). In addition, SMX degradation through UV pretreatment followed by ozonation in the presence of HA was proved to be an effective method which can remove SMX with a low ozone dose. The results suggested that ozonation of SMX was more affected by concentration of influent ozone gas, alkalinity, and HA, while incident UV light intensity, pH, and HA were the dominant factors influencing UV degradation of SMX.
研究了在不同参数下,包括进水臭氧气体浓度、初始磺胺甲恶唑(SMX)浓度、紫外光强度、离子强度、不同阴离子(碳酸氢盐、硫酸盐和硝酸盐)、腐殖酸(HA)和 pH 值等水质条件下,臭氧氧化和 UV(254)辐射对磺胺甲恶唑降解的速率常数。结果表明,臭氧氧化和 UV(254)辐射对 SMX 的去除均符合准一级动力学模型,速率常数的范围分别为(0.9-9.8)×10(-3)和(1.7-18.9)×10(-3)s(-1)。还确定了在不同操作参数下,SMX 与臭氧的二级速率常数(ko(3)),其范围为(0.60-3.38)±0.13×10(5)M(-1)s(-1)。此外,证明了在 HA 存在下,通过 UV 预处理然后进行臭氧氧化的方法是去除低臭氧剂量 SMX 的有效方法。结果表明,臭氧氧化 SMX 受进水臭氧气体浓度、碱度和 HA 的影响更大,而入射紫外光强度、pH 值和 HA 是影响 SMX 紫外降解的主要因素。