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不同组成水样和废水中的萘啶酸的太阳光芬顿降解。通过 LC-TOF-MS 进行的分析评估。

Solar photo-Fenton degradation of nalidixic acid in waters and wastewaters of different composition. Analytical assessment by LC-TOF-MS.

机构信息

Plataforma Solar de Almería, CIEMAT, Carretera Senés, km 4, 04200 Tabernas, Almería, Spain.

出版信息

Water Res. 2011 Feb;45(4):1736-44. doi: 10.1016/j.watres.2010.11.023. Epub 2010 Nov 24.

DOI:10.1016/j.watres.2010.11.023
PMID:21146848
Abstract

This work assessed the solar photo-Fenton degradation of nalidixic acid (NXA), a quinolone antibacterial agent, in several different aqueous solutions. It has been proven that the composition of the water clearly affects the efficiency of the photo-Fenton process. The presence of chlorine ions induces the concurrence of different mechanisms involving Cl() and Cl(2)(-) radicals, which slow down the process. Up to 35 transformation products (TPs) were identified and their structures characterized by accurate LC-TOF-MS mass measurements during treatment of the different model waters. Photocatalytic degradation was thus observed to proceed mainly through the attack of the hydroxyl radicals on the double bond C((2))C((3)) which induce further ring opening. All the TPs identified persisted after total degradation of NXA. NXA in real pharmaceutical effluent was treated by photo-Fenton as a first stage before biological treatment. As NXA has been demonstrated to be recalcitrant to biological treatment, photo-Fenton treatment of the effluent was continued until its total degradation. Although NXA was efficiently degraded, LC-MS analyses demonstrated that some of the TPs identified after the photo-Fenton treatment were also recalcitrant to biological treatment, persisting after the combined treatment. These results show that analytical assessment of photocatalytic water treatments is essential to assure they are functioning as intended.

摘要

本工作评估了几种不同水溶液中萘啶酸(NXA)的太阳光芬顿降解。已经证明,水的组成明显影响光芬顿过程的效率。氯离子的存在诱导涉及 Cl()和 Cl(2)(-)自由基的不同机制同时发生,从而减缓了该过程。在处理不同模型水时,通过准确的 LC-TOF-MS 质量测量,共鉴定出 35 种转化产物(TPs)并对其结构进行了表征。因此,观察到光催化降解主要通过羟基自由基对双键 C((2))C((3))的攻击进行,这进一步导致了环的打开。在 NXA 的完全降解后,所有鉴定的 TPs 仍然存在。实际制药废水中的 NXA 先经过光芬顿处理,然后再进行生物处理。由于已经证明 NXA 难以进行生物处理,因此继续对废水进行光芬顿处理,直到其完全降解。尽管 NXA 被有效地降解,但 LC-MS 分析表明,在光芬顿处理后鉴定出的一些 TPs 也难以进行生物处理,在联合处理后仍然存在。这些结果表明,对光催化水处理的分析评估对于确保其按预期运行至关重要。

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