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使用芬顿氧化法降解环丙沙星:操作参数的影响、氧化副产物的鉴定和毒性评估。

Degradation of ciprofloxacin using Fenton's oxidation: Effect of operating parameters, identification of oxidized by-products and toxicity assessment.

机构信息

Centre for Environmental Science and Engineering, Indian Institute of Technology Bombay, Powai, Mumbai, India.

Centre for Environmental Science and Engineering, Indian Institute of Technology Bombay, Powai, Mumbai, India.

出版信息

Chemosphere. 2018 Feb;193:1181-1188. doi: 10.1016/j.chemosphere.2017.11.046. Epub 2017 Nov 13.

DOI:10.1016/j.chemosphere.2017.11.046
PMID:29874747
Abstract

Ciprofloxacin (CPX), a fluoroquinolone antibiotic, is found in the bulk effluents emerged from pharmaceutical industries. Its presence in the effluent may lead to toxicity to the aquatic life and antimicrobial resistance. Hence, the oxidative degradation of CPX by classical Fenton's process was investigated for the present study. The maximum CPX and total organic carbon (TOC) removal from the synthetic wastewater (initial CPX concentration = 100 mg L) were 70% and 55%, respectively, under the best reaction conditions ([HO]:[Fe] = 10, stoichiometric HO concentration = 14.2 mM and initial wastewater pH = 3.0). Five major degradation products could be identified by high resolution liquid chromatography-mass spectrometry (HR LC-MS) which could have resulted by the occurrence of decarboxylation, defluorination, hydroxylation and cleavage of the piperazine ring. The time based detection of ferrous and ferric ions in aqueous phase confirmed the CPX degradation by hydroxyl radicals. A pathway has been proposed for CPX degradation by Fenton's process based on the kinetic decay and/or evolution profiles of CPX and intermediates as well as the release of inorganic ions into the aqueous solution. It was indicated from the rapid respirometric test that the wastewater toxicity was lowered after Fenton's treatment.

摘要

环丙沙星(CPX)是一种氟喹诺酮类抗生素,存在于制药工业产生的大量废水中。其存在于废水中可能会对水生生物产生毒性和导致抗药性。因此,本研究考察了经典芬顿法对 CPX 的氧化降解作用。在最佳反应条件下([HO]:[Fe] = 10,化学计量 HO 浓度 = 14.2 mM,初始废水 pH = 3.0),从合成废水中(初始 CPX 浓度为 100 mg L),CPX 的最大去除率和总有机碳(TOC)去除率分别为 70%和 55%。通过高分辨率液相色谱-质谱(HR LC-MS)鉴定了 5 种主要降解产物,它们可能是通过脱羧、脱氟、羟化和哌嗪环断裂而产生的。通过检测水相中亚铁离子和铁离子的时间依赖性,证实了 CPX 是通过羟基自由基降解的。根据 CPX 和中间产物的动力学衰减和/或演化谱以及无机离子在水溶液中的释放情况,提出了芬顿法降解 CPX 的途径。快速呼吸计量试验表明,芬顿处理后废水毒性降低。

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