A low-cost iron mining residue catalyst employed in antibiotic degradation: Parameter optimization, influence of photogenerated species and the identification of main transformation products

残留物(化学) 降级(电信) 催化作用 转化(遗传学) 化学 抗生素 鉴定(生物学) 化学工程 组合化学 生化工程 制浆造纸工业 计算机科学 有机化学 生物化学 工程类 生态学 生物 基因 电信
作者
Michelle Reis da Silva,Deivisson Lopes Cunha,Alexei Kuznetsov,Joyce R. Araújo,Alexandre Della-Flora,Alexsandro Dallegrave,Carla Sirtori,Enrico Mendes Saggioro
出处
期刊:Journal of environmental chemical engineering [Elsevier]
卷期号:12 (1): 111844-111844
标识
DOI:10.1016/j.jece.2023.111844
摘要

The ubiquitous presence of antibiotics in aquatic ecosystems due to their frequent and indiscriminate use has become a major global health concern, leading to high environmental bacteria and resistance gene development. In this context, this study aimed to evaluate the degradation of three antibiotics, ciprofloxacin (CIP), sulfamethoxazole (SMX) and tetracycline (TET), employing a mining residue as the photocatalyst. The mining residue was characterized by the Brunauer-Emmett-Teller (BET), X ray photoelectron spectroscopy (XPS), scanning electron microscopy (SEM), X ray diffraction (XRD) techniques, and exhibited high iron content (∼70%) predominantly Fe+2. A rotatable central composite design (RCCD) employing catalyst concentrations, H2O2 and pH as variables was applied, resulting in optimal catalyst and H2O2 concentrations of 277.01 mg L−1 and 65.37 mg L−1, respectively, at pH 3.4. These conditions achieved 89% and 83% SMX and CIP degradation rates and the TET concentration at 60 min of treatment was lower than the instrumental LOD, confirming the predominance of catalyst photo-Fenton reactions. When applied to a real effluent sample, 71% and 79% SMX and CIP degradation rates were observed, respectively, while no degradation value changes were noted for TET at 60 min. The main reactive species involved in the antibiotic degradation reactions were HO• for SMX, O2•- and h+ for CIP, and O2•- for TET. In total, 12 antibiotic transformation products (TPs) were identified by LC-QTOF MS. The most frequent TPs observed during antibiotic degradation were formed by hydroxylation, dealkylation, defluorination and hydrolysis of the sulfonamide bond. The investigated mining residue is, therefore, a low-cost and efficient alternative for the photocatalytic degradation of CIP, SMX and TET, contributing to the United Nations Sustainable Development Goals (SDG 6) and follows circular economy principles.
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