School of Environment, Tsinghua University, Beijing, 100084, China; Beijing Key Laboratory for Emerging Organic Contaminants Control, Tsinghua University, Beijing, 100084, China; State Key Joint Laboratory of Environmental Simulation and Pollution Control, Tsinghua University, Beijing, 100084, China.
School of Environment, Tsinghua University, Beijing, 100084, China; Beijing Key Laboratory for Emerging Organic Contaminants Control, Tsinghua University, Beijing, 100084, China.
Chemosphere. 2019 Dec;236:124374. doi: 10.1016/j.chemosphere.2019.124374. Epub 2019 Jul 15.
The degradation of irgarol, a frequently detected algaecide in the aquatic environment, by ozonation was investigated in this study. The second-order rate constants for the reaction of irgarol with ozone (O) and hydroxyl radical (OH) were determined to be 505 M s and 4.96 × 10 M s, respectively. During ozonation, sixteen transformation products (TPs) of irgarol were proposed using an electrospray ionization quadrupole time-of-flight mass spectrometer. Most of the TPs are ozone-refractory compounds and therefore could only be further transformed by oxidation with OH generated from O decomposition during ozonation. Toxicity analysis using the ecological structure activity relationship class program indicates that some of the TPs (e.g., irgarol sulfoxide) still exhibit high acute or chronic toxicity to aquatic organisms (fish, daphnia, and algae) as the parent compound. With a typical ozone dose applied in water treatment (2 mg/L, corresponding to a specific ozone dose of 0.8 mg O/mg dissolved organic carbon), irgarol could be completely abated in a selected surface water by ozonation. However, most of the TPs persisted in the ozonation effluent because of their low ozone reactivity. The results of this study suggest that ozonation with typical ozone doses applied in water treatment may not be able to sufficiently reduce the ecotoxicological effects of irgarol on aquatic organisms. More effective treatment processes such as ozone-based advanced oxidation processes may be required to enhance the removal of toxic TPs of irgarol in water treatment.
本研究考察了臭氧氧化法降解水体中常见杀藻剂——敌草快的反应过程。实验测定了敌草快与臭氧(O)和羟基自由基(OH)的二级反应速率常数,分别为 505 M s 和 4.96×10 M s。在臭氧氧化过程中,利用电喷雾电离四极杆飞行时间质谱仪提出了 16 种敌草快转化产物(TPs)。大多数 TPs 为臭氧难降解化合物,因此只能在臭氧分解过程中生成的 OH 进一步氧化下转化。采用生态结构活性关系类程序进行毒性分析表明,部分 TPs(如敌草快亚砜)仍表现出对水生生物(鱼类、水蚤和藻类)的高急性或慢性毒性,与母体化合物相当。在水处理中应用典型臭氧剂量(2 mg/L,相当于 0.8 mg O/mg 溶解有机碳的特定臭氧剂量)时,敌草快可在选定的地表水中完全消除。然而,由于其臭氧反应性低,大多数 TPs 仍会残留在臭氧氧化后的废水中。研究结果表明,在水处理中应用典型臭氧剂量的臭氧氧化法可能无法充分降低敌草快对水生生物的生态毒性效应。为了增强水中敌草快毒性 TPs 的去除效果,可能需要更有效的处理工艺,如臭氧基高级氧化工艺。