Vogna Davide, Marotta Raffaele, Napolitano Alessandra, Andreozzi Roberto, d'Ischia Marco
Dip. di Chimica Organica e Biochimica, Federico II, Facolta di Scienze, Universita degli Studi di Napoli Complesso Universitario M. S. Angelo, via Cinthia, 4, 80126, Napoli, Italy.
Water Res. 2004 Jan;38(2):414-22. doi: 10.1016/j.watres.2003.09.028.
Diclofenac, a widely used anti-inflammatory drug, has been found in many Sewage Treatment Plant effluents, rivers and lake waters, and has been reported to exhibit adverse effects on fish. Advanced oxidation processes, ozonation and H2O2/UV were investigated for its degradation in water. The kinetic of the degradation reaction and the nature of the intermediate products were still poorly defined. Under the conditions adopted in the present study, both ozonation and H2O2/UV systems proved to be effective in inducing diclofenac degradation, ensuring a complete conversion of the chlorine into chloride ions and degrees of mineralization of 32% for ozonation and 39% for H2O2/UV after a 90 min treatment. The reactions were found to follow similar, but not identical, reaction pathways leading to hydroxylated intermediates (e.g. 2-[(2,6-dichlorophenyl)amino]-5-hydroxyphenylacetic acid) and C-N cleavage products (notably 2,5-dihydroxyphenylacetic acid) through competitive routes. Subsequent oxidative ring cleavage leads to carboxylic acid fragments via classic degradation pathways. In the pH range 5.0-6.0 kinetic constants (1.76 x 10(4)-1.84 x 10(4) M(-1) s(-1)) were estimated for diclofenac ozonation.
双氯芬酸是一种广泛使用的抗炎药物,已在许多污水处理厂的废水、河流和湖泊水中被检测到,据报道它对鱼类有不良影响。研究了高级氧化工艺、臭氧化和过氧化氢/紫外线对水中双氯芬酸的降解作用。降解反应的动力学和中间产物的性质仍不清楚。在本研究采用的条件下,臭氧化和过氧化氢/紫外线系统均被证明能有效诱导双氯芬酸降解,确保氯完全转化为氯离子,经过90分钟处理后,臭氧化的矿化度为32%,过氧化氢/紫外线的矿化度为39%。发现这些反应遵循相似但不完全相同的反应途径,通过竞争途径生成羟基化中间体(如2-[(2,6-二氯苯基)氨基]-5-羟基苯乙酸)和碳氮裂解产物(特别是2,5-二羟基苯乙酸)。随后的氧化开环通过经典降解途径产生羧酸片段。在pH值5.0-6.0范围内,估计双氯芬酸臭氧化的动力学常数为(1.76×10⁴-1.84×10⁴ M⁻¹ s⁻¹)。