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首页> 外文期刊>Applied Catalysis, B. Environmental: An International Journal Devoted to Catalytic Science and Its Applications >Degradation of the antibiotic trimethoprim by electrochemical advanced oxidation processes using a carbon-PTFE air-diffusion cathode and a boron-doped diamond or platinum anode
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Degradation of the antibiotic trimethoprim by electrochemical advanced oxidation processes using a carbon-PTFE air-diffusion cathode and a boron-doped diamond or platinum anode

机译:使用碳-PTFE空气扩散阴极和掺硼金刚石或铂阳极通过电化学高级氧化工艺降解抗生素甲氧苄啶

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The degradation of 20.0 mg L~(-1) of trimethoprim (TMP), an antibiotic commonly detected in wastewaters, in an aqueous solution with 7.0gL~(-1) Na2S04 was accomplished by electrochemical advanced oxidation processes (EAOPs) such as anodic oxidation with electrogenerated H2O2 (AO-H2O2), electro-Fenton (EF), photoelectro-Fenton (PEF) and solar photoelectro-Fenton (SPEF), as well as by the classical Fenton and photo-Fenton processes. All experiments were performed in a novel 2.2 L lab-scale flow plant equipped with compound parabolic collectors (CPCs) and an electrochemical filter-press cell with a BDD or Pt anode and a carbon-PTFE air-diffusion cathode to electrogenerate H2O2. The effect of initial Fe~(2+) concentration, current density and pH on the PEF method with the BDD anode (PEF-BDD) was firstly assessed by means of TMP and dissolved organic carbon (DOC) decays, aiming to establish a treatment process using minimal iron concentration, adequate current density/H2O2 production and maximal pH. This treatment was efficiently performed using a low Fe~(2+) dose of 2.0 mg L~(-1), a low current density of 5 mA cm~(-2) and pH of 3.5 without iron precipitation. The relative oxidation ability of EAOPs using the BDD/air-diffusion cell increased in the order: AO-H2O2 < EF < PEF < SPEF. The EF-BDD and PEF-BDD processes were more effective than the comparable Fenton and photo-Fenton ones. The PEF-BDD process exhibited slightly faster TMP degradation than the PEF-Pt one, whereas in SPEF the influence of the anode was almost negligible. After ca. 37 kJ L~(-1) UV energy, 77 and 73% mineralization with 30 and 26% current efficiency and 1.2 and 0.9 kWh m~(-30 energy cost were obtained, respectively. It was found a slow and partial TMP mineralization mainly linked to the formation of a high content of hardly oxidizable N-derivatives, containing the major part of N. Up to 18 aromatic products and 19 hydroxylated derivatives were detected by LC-MS during TMP degradation by PEF-Pt. An additional SPEF-Pt experiment using a real wastewater matrix spiked with TMP attained slower TMP and DOC decays.
机译:通过电化学高级氧化工艺(EAOPs)(例如阳极氧化)可在含有7.0gL〜(-1)Na2SO4的水溶液中降解20.0 mg L〜(-1)的甲氧苄啶(TMP)(一种常见于废水中的抗生素)。用电生成的H2O2(AO-H2O2),电Fenton(EF),光电Fenton(PEF)和太阳能光电Fenton(SPEF)以及传统的Fenton和Photo-Fenton工艺进行氧化。所有实验均在新型的2.2 L实验室规模的流动装置中进行,该流动装置配备有复合抛物线收集器(CPC)和带有BDD或Pt阳极和碳PTFE空气扩散阴极的电化学压滤单元,可产生H2O2。首先通过TMP和溶解有机碳(DOC)的衰减来评估初始Fe〜(2+)浓度,电流密度和pH值对使用BDD阳极(PEF-BDD)的PEF方法的影响,以建立一种处理方法。使用最小的铁浓度,足够的电流密度/ H2O2产生量和最大pH值的过程。使用2.0 mg L〜(-1)的低Fe〜(2+)剂量,5 mA cm〜(-2)的低电流密度和3.5的pH值而无铁沉淀有效地进行了该处理。使用BDD /空气扩散池的EAOP的相对氧化能力按以下顺序增加:AO-H2O2

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