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UV 和 UV/过硫酸盐工艺在蒸馏水中和模拟医院废水中对高消耗的氟喹诺酮类、青霉素类和头孢菌素类的降解。

Degradation of highly consumed fluoroquinolones, penicillins and cephalosporins in distilled water and simulated hospital wastewater by UV and UV/persulfate processes.

机构信息

Grupo de Investigación en Remediación Ambiental y Biocatálisis (GIRAB), Instituto de Química, Facultad de Ciencias Exactas y Naturales, Universidad de Antioquia UdeA, Calle 70 No. 52-21, Medellín, Colombia.

Departamento de Ciencias Básicas, Universidad Católica Luis Amigó, Transversal 51A No. 67B-90, Medellín, Colombia.

出版信息

Water Res. 2017 Oct 1;122:128-138. doi: 10.1016/j.watres.2017.05.065. Epub 2017 Jun 1.

Abstract

In this work, three penicillins (ampicillin "AMP", oxacillin "OXA" and cloxacillin "CLO"), two cephalosporins (cephalexin "CPX" and cephadroxyl "CPD") and three fluoroquinolones (levofloxacin "LEV", norfloxacin "NOR" and ciprofloxacin "CIP") were initially treated by UV and persulfate activated by UV (UV/PS). Significant differences in degradation kinetics under UV irradiation were found. Photodegradation followed the order: OXA > CPX > CPD > CLO > CIP > NOR > AMP ≫ LEV. Then, in order to study the participation of direct photolysis and reactive oxygen species (ROS) in photodegradation a model antibiotic of each class (OXA, CPX and CIP) was considered. OXA and CPX were mainly degraded by direct photolysis, whereas the CIP removal involved ROS and photolysis. On the other hand, the persulfate addition (UV/PS process) improved the removals due to sulfate radical formation, especially, in the case of antibiotics with lower photodegradation levels (i.e. LEV, AMP and NOR). Computational calculations on the representative antibiotics were applied to determine the regions susceptible to electrophilic attacks by degrading agents. The functional groups of OXA and CPX followed the reactivity order: thioether ≫ β-lactam ring > benzene ring. For CIP, the piperazyl moiety presented higher reactivity than the quinolone ring. Also, the antimicrobial activity (AA) evolution during the treatments was tested. In the cases of CPX and CIP, both UV and UV/PS removed the AA; which were associated with structural changes in their reactive moieties: β-lactam ring and piperazyl ring, respectively. However, in the case of OXA only the UV/PS system decreased AA, which was attributed to transformations in its penicillin electron-rich nucleus (thioether + β-lactam). Finally, the applicability of UV and UV/PS was assessed using synthetic hospital wastewater (HWW). The processes comparison showed that for practical purposes, OXA and CIP in HWW should be treated by UV/PS, while CPX in HWW could be treated by both UV and UV/PS.

摘要

在这项工作中,我们最初用紫外线和过硫酸盐(UV/PS)处理了三种青霉素(氨苄西林“AMP”、苯唑西林“OXA”和氯唑西林“CLO”)、两种头孢菌素(头孢氨苄“CPX”和头孢羟氨苄“CPD”)和三种氟喹诺酮类药物(左氧氟沙星“LEV”、诺氟沙星“NOR”和环丙沙星“CIP”)。在紫外线照射下,降解动力学有显著差异。光降解的顺序为:OXA > CPX > CPD > CLO > CIP > NOR > AMP ≫ LEV。然后,为了研究直接光解和活性氧物种(ROS)在光降解中的参与,考虑了每种类别的模型抗生素(OXA、CPX 和 CIP)。OXA 和 CPX 主要通过直接光解降解,而 CIP 的去除则涉及 ROS 和光解。另一方面,过硫酸盐的添加(UV/PS 工艺)提高了去除率,因为形成了硫酸根自由基,特别是对于光降解水平较低的抗生素(即 LEV、AMP 和 NOR)。对代表性抗生素进行了计算计算,以确定易受降解剂亲电攻击的区域。OXA 和 CPX 的官能团遵循反应性顺序:硫醚 ≫ β-内酰胺环 > 苯环。对于 CIP,哌嗪部分的反应性高于喹诺酮环。此外,还测试了处理过程中抗菌活性(AA)的演变。在 CPX 和 CIP 的情况下,UV 和 UV/PS 都去除了 AA;这与它们的反应性部分的结构变化有关:β-内酰胺环和哌嗪环。然而,在 OXA 的情况下,只有 UV/PS 系统降低了 AA,这归因于其青霉素富电子核(硫醚 + β-内酰胺)的转化。最后,使用合成医院废水(HWW)评估了 UV 和 UV/PS 的适用性。过程比较表明,对于实际目的,HWW 中的 OXA 和 CIP 应通过 UV/PS 处理,而 HWW 中的 CPX 可以通过 UV 和 UV/PS 处理。

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