臭氧氧化水溶液中对乙酰氨基酚的机制研究

Impact Factors and Degradation Mechanism for the Ozonation of Acetaminophen in Aqueous Solution

采用间歇实验的方法,研究了臭氧氧化降解水溶液中对乙酰氨基酚的影响因素和机制.结果表明,臭氧能够有效降解水溶液中的对乙酰氨基酚,降解过程符合伪一级动力学模型(R2>0.992).臭氧浓度、HCO-3和pH值均影响对乙酰氨基酚的降解过程,添加HCO-3、提高pH值和适当增大臭氧浓度均可提高其降解效果.气相色谱/质谱和离子色谱检测结果表明,在对乙酰氨基酚臭氧氧化的过程中,首先生成对苯酚及一系列含有羧基的酸类产物,继而被进一步氧化;依据中间产物,探讨了对乙酰氨基酚可能的降解反应途径.TOC检测仪的检测结果显示,对乙酰氨基酚的最终矿化程度较低.在对乙酰氨基酚的初始浓度为20 mg·L-1及臭氧浓度为9.10 mg·L-1时,反应130 min后,矿化程度仅为16.42%.

The effect and mechanism of O3 on the degradation of acetaminophen in aqueous solution were studied by the batch experiment. The results showed that acetaminophen could be degraded effectively by ozone and degradation of acetaminophen fitted well with the pseudo-first-order kinetics model(R2> 0. 992). The degradation of acetaminophen was promoted with the increase of pH,the concentration of bicarbonate and ozone. The results of gas chromatography-mass spectrometry( GC-MS) and ion chromatography analysis showed that degradation products such as hydroquinone and a series of carboxylic acids were firstly formed during ozonation of acetaminophen. Then,the products were further oxidized. The degradation pathways of acetaminophen were also discussed by the identified products. The result of TOC showed that the mineralization of acetaminophen was ultimately lower. When the initial concentration of acetaminophen was 20 mg·L- 1and the concentration of ozone was 9. 10 mg·L- 1,the mineralization was only 16.42%after 130 min.