Sági Gyuri, Csay Tamás, Szabó László, Pátzay György, Csonka Emil, Takács Erzsébet, Wojnárovits László
Institute for Energy Security and Environmental Safety, Centre for Energy Research, Hungarian Academy of Sciences, 1121, Konkoly-Thege Miklós út 29-33, Budapest, Hungary.
Institute for Energy Security and Environmental Safety, Centre for Energy Research, Hungarian Academy of Sciences, 1121, Konkoly-Thege Miklós út 29-33, Budapest, Hungary.
J Pharm Biomed Anal. 2015 Mar 15;106:52-60. doi: 10.1016/j.jpba.2014.08.028. Epub 2014 Sep 16.
By combining a large variety of analytical techniques this study aimed at elaborating methods to follow up the degradation of sulfonamides in an advanced oxidation process (AOP): irradiation with ionizing radiation in dilute aqueous solution. In this process, besides other radicals, hydroxyl radicals are produced. As pulse radiolysis experiments show the basic initial reaction is hydroxyl radical addition to the benzene ring, forming cyclohexadienyl radical intermediates. In aerated solutions these radicals transform to peroxy radicals. Among the first formed products aromatic molecules hydroxylated in the benzene rings or in some cases in the heterocyclic rings were observed by LC-MS/MS. Chemical oxygen demand (COD) measurements indicate that at the early reaction period of degradation one hydroxyl radical induces incorporation of 1.5 O atoms into the products. Comparison of the COD and TOC (total organic carbon content) results shows gradual oxidation. Simultaneously with hydroxylation ring opening also takes place. The kinetics of inorganic SO4(2-) and NH4(+) formation, analyzed by ion chromatography, is similar to the kinetics of ring degradation (UV spectroscopy), however, there is a delayed formation of NO3(-). The latter ions may be produced in oxidative degradation of smaller N containing fragments. The S atoms of the sulfonamides remain in the solution (ICP-MS measurements) after degradation, whereas some part of the N atoms leaves the solution probably in the form of N2 (total nitrogen content (TN) measurements). Degradation is accompanied by a high pH drop due to formation of SO4(2-), NO3(-) and smaller organic acids. The degradation goes through many simultaneous and consecutive reactions, and with the applied methods the different stages of degradation can be characterized.
通过结合多种分析技术,本研究旨在阐述在高级氧化过程(AOP)中跟踪磺胺类药物降解的方法:在稀水溶液中进行电离辐射照射。在此过程中,除了其他自由基外,还会产生羟基自由基。脉冲辐解实验表明,基本的初始反应是羟基自由基加成到苯环上,形成环己二烯基自由基中间体。在曝气溶液中,这些自由基会转化为过氧自由基。通过LC-MS/MS观察到,在最初形成的产物中,有苯环或某些情况下杂环被羟基化的芳香分子。化学需氧量(COD)测量表明,在降解的早期反应阶段,一个羟基自由基会促使1.5个氧原子掺入产物中。COD和TOC(总有机碳含量)结果的比较显示出逐渐氧化的过程。与羟基化同时发生的还有开环反应。通过离子色谱分析无机SO4(2-)和NH4(+)形成的动力学,与环降解动力学(紫外光谱)相似,然而,NO3(-)的形成存在延迟。后者的离子可能是在较小含氮片段的氧化降解过程中产生的。磺胺类药物的S原子在降解后保留在溶液中(ICP-MS测量),而一些N原子可能以N2的形式离开溶液(总氮含量(TN)测量)。由于SO4(2-)、NO3(-)和较小有机酸的形成,降解过程伴随着pH值的大幅下降。降解过程经历了许多同时发生和连续的反应,并且通过所应用的方法可以表征降解的不同阶段。