Ma Du-juan, Liu Guo-guang, Lü Wen-ying, Yao Kun, Zhou Li-hua, Xie Cheng-ping
School of Environmental Science and Engineering, Guangdong University of Technology, Guangzhou 510006, China.
Huan Jing Ke Xue. 2013 May;34(5):1782-9.
This paper studies the degradation mechanism, the reaction kinetics and the toxicity of photolysis products of naproxen in waters under UV irradiation (120 W mercury lamp) by quenching experiments of reactive oxygen species (ROS), oxygen concentration experiment and toxicity evaluation using Vibrio fischeri bacteria. The results demonstrated that NPX could be degraded effectively by UV irradiation and the photolysis pathways was the sum of the degradation by direct photolysis and self-sensitization via ROS, and the contribution rates of self-sensitized photodegradation were 0.1%, 80.2%, 35.7% via OH, (1)O2, O2-, respectively. The effect of oxygen concentration illustrated that dissolved oxygen had an inhibitory effect on the direct photodegradation of NPX, and the higher the oxygen content, the more obvious the inhibitory effect. The toxicity evaluation illustrated the formation of some intermediate products that were more toxic than NPX during the photodegradation of NPX. The process of NPX degradation in all cases could be fitted by the pseudo first-order kinetics model.
本文通过活性氧(ROS)猝灭实验、氧浓度实验以及使用费氏弧菌进行毒性评估,研究了紫外光(120W汞灯)照射下水中萘普生的降解机理、反应动力学及光解产物的毒性。结果表明,萘普生可通过紫外光有效降解,光解途径为直接光解和通过ROS的自敏化降解之和,通过OH、(1)O2、O2-的自敏化光降解贡献率分别为0.1%、80.2%、35.7%。氧浓度的影响表明,溶解氧对萘普生的直接光降解有抑制作用,氧含量越高,抑制作用越明显。毒性评估表明,萘普生光降解过程中会形成一些比萘普生毒性更强的中间产物。所有情况下萘普生的降解过程都可以用伪一级动力学模型拟合。