臭氧氧化降解水中磺胺嘧啶的机理研究

Degradation mechanisms of sulfadiazine in aqueous solution by ozonation

  • 摘要: 环境中残留的抗生素药物对生态环境的危害受到极大关注。研究了臭氧对水中磺胺嘧啶(SD)的降解,考察了溶液pH、臭氧浓度和HC O 3 - 投加量对臭氧降解SD的影响,并对其降解机理进行了分析。结果表明:初始pH、臭氧浓度及HC O 3 - 均对臭氧氧化降解SD过程造成影响,提高pH、增加臭氧浓度和HC O 3 - 投加量均能提高SD降解速率;在SD浓度为30 mg/L、初始pH为9.14、臭氧浓度为10.0 mg/L、HC O 3 - 投加量为100 mg/L时,反应30 min后SD基本被去除,120 min后SD的最终矿化率为39.44%;臭氧降解SD过程基本符合伪一级动力学模型。液相色谱-质谱分析结果显示:臭氧氧化SD过程中,生成中间产物对氨基苯磺酸(C6H7NO3S),经臭氧进一步氧化分解,最终矿化生成CO2

     

    Abstract: The harm of antibiotics in the environment is of great concern to the ecological environment. The degradation of sulfadiazine (SD) by ozone was studied. The effects of pH, ozone concentration and HC O 3 - concentration on the degradation of SD were investigated, and the degradation mechanisms were also analyzed. The results showed that the initial pH, the ozone concentration and HC O 3 - all had effects on the SD degradation process, and the initial pH, the ozone concentration and HC O 3 - concentration could increase the degradation rate of SD. At initial pH of 9.14, SD concentration of 30 mg/L, ozone concentration of 10.0 mg/L and HC O 3 - dosage of 100 mg/L, the SD was primarily removed after a reaction time of 30 min and finally reached a mineralization rate of 39.44% at 120 min. The SD process of ozone degradation was basically in accordance with pseudo-first-order kinetics model. The results of liquid chromatography-mass spectrometry showed that, in the course of ozone oxidation, the formation of p-aminobenzenesulfonic acid (C6H7NO3S) was produced and being further oxidized by ozone and finally mineralized to form CO2.

     

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