Grupo de Investigación en Remediación Ambiental y Biocatálisis (GIRAB), Instituto de Química, Facultad de Ciencias Exactas y Naturales, Universidad de Antioquía UdeA, Calle 70 No. 52-21, Medellin, Colombia.
Environ Sci Pollut Res Int. 2017 Dec;24(36):28175-28189. doi: 10.1007/s11356-017-0404-5. Epub 2017 Oct 10.
Taking ciprofloxacin (CIP) as a fluoroquinolone antibiotic model, this work explores the role of common anions (sulfate, nitrate, and chloride) during the application of photoelectro-Fenton (PEF) at natural pH to degrade this type of compound in water. The system was composed of an IrO anode, Ti, or gas diffusion electrode (GDE) as cathode, Fe, and UV (254 nm). To determine the implications of these anions, the degradation pathway and efficiency of the PEF sub-processes (UV photolysis, anodic oxidation, and electro-Fenton at natural pH) were studied in the individual presence of the anions. The results highlight that degradation routes and kinetics are strongly dependent on electrolytes. When chloride and nitrate ions were present, indirect electro-chemical oxidation was identified by electro-generated HOCl and nitrogenated oxidative species, respectively. Additionally, direct photolysis and direct oxidation at the anode surface were identified as degradation routes. As a consequence of the different pathways, six primary CIP by-products were identified. Therefore, a scheme was proposed representing the pathways involved in the degradation of CIP when submitted to PEF in water with chloride, nitrate, and sulfate ions, showing the complexity of this process. Promoted by individual and synergistic actions of this process, the PEF system leads to a complete elimination of CIP with total removal of antibiotic activity against Staphylococcus aureus and Escherichia coli, and significant mineralization. Finally, the role of the anions was tested in seawater containing CIP, in which the positive contributions of the anions were partially suppressed by its OH radical scavenger action. The findings are of interest for the understanding of the degradation of antibiotics via the PEF process in different matrices containing sulfate, nitrate, and chloride ions.
以环丙沙星(CIP)作为氟喹诺酮类抗生素模型,本工作探索了在自然 pH 值下应用光电芬顿(PEF)降解水中此类化合物时常见阴离子(硫酸盐、硝酸盐和氯化物)的作用。该系统由 IrO 阳极、Ti 或气体扩散电极(GDE)作为阴极、Fe 和 UV(254nm)组成。为了确定这些阴离子的影响,在单独存在阴离子的情况下,研究了 PEF 亚过程(UV 光解、阳极氧化和自然 pH 值下的电芬顿)的降解途径和效率。结果表明,降解途径和动力学强烈依赖于电解质。当存在氯离子和硝酸盐离子时,分别通过电生成的 HOCl 和含氮氧化物种确定了间接电化学氧化。此外,还确定了直接光解和阳极表面的直接氧化为降解途径。由于不同的途径,鉴定出六种主要的 CIP 中间产物。因此,提出了一个方案,代表了在水中存在氯离子、硝酸盐和硫酸盐时,CIP 受到 PEF 降解的途径,展示了这个过程的复杂性。在这个过程的单独和协同作用的推动下,PEF 系统导致 CIP 的完全消除,对金黄色葡萄球菌和大肠杆菌的抗生素活性完全去除,以及显著的矿化。最后,在含有 CIP 的海水中测试了阴离子的作用,其中阴离子的积极作用部分被其 OH 自由基清除剂作用所抑制。这些发现对于理解在含有硫酸盐、硝酸盐和氯离子的不同基质中通过 PEF 过程降解抗生素具有重要意义。