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利用活性污泥生物量制备的酸改性生物炭从单组份和双组份水体系中吸附磺胺甲恶唑和林可霉素。

Adsorption of sulfamethoxazole and lincomycin from single and binary aqueous systems using acid-modified biochar from activated sludge biomass.

机构信息

Department of Chemical and Biological Engineering, University of Saskatchewan, Saskatoon, Saskatchewan, Canada.

Department of Chemical and Biological Engineering, University of Saskatchewan, Saskatoon, Saskatchewan, Canada; Global Institute for Water Security, University of Saskatchewan, Saskatoon, Saskatchewan, Canada.

出版信息

J Environ Manage. 2024 May;358:120742. doi: 10.1016/j.jenvman.2024.120742. Epub 2024 Apr 8.

Abstract

The extensive use of pharmaceuticals has raised growing concerns regarding their presence in surface waters. High concentrations of sulfamethoxazole (SMX) and lincomycin (LIN), as commonly prescribed antibiotics, persist in various wastewaters and surface waters, posing risks to public health and the environment. Biochar derived from accessible biowaste, like activated sludge biomass, offers a sustainable and eco-friendly solution to mitigate antibiotic release into water systems. This study investigates the effectiveness of HPO-modified activated sludge-based biochar (PBC) synthesized through microwave (MW) heating for the adsorption of SMX and LIN antibiotics. The synthesis parameters of PBC were optimized using a central composite design considering MW power, time, and HPO concentration. Characterization results validate the efficacy of the synthesis process creating a specific surface area of 365 m/g, and well-developed porosity with abundant oxygen-containing functional groups. Batch and dynamic adsorption experiments were piloted to assess the adsorption performance of PBC in single and binary antibiotic systems. Results show that PBC exhibits a higher affinity for SMX rather than LIN, with maximum adsorption capacities of 45.6 mg/g and 26.6 mg/g, respectively. Based on kinetic studies chemisorption is suggested as the primary mechanism for SMX and LIN removal. Equilibrium studies show a strong agreement with the Redlich-Peterson isotherm, suggesting a composite adsorption mechanism with a greater probability of multilayer adsorption for both antibiotics. Hydrogen bonding and π-π electron sharing are suggested as the prevailing adsorption mechanisms of SMX and LIN on the modified biochar. Furthermore, a dynamic adsorption system was replicated using a fixed bed column setup, demonstrating effective removal of SMX and LIN from pure water and real wastewater samples using PBC-loaded hydrogel beads (PBC-B). These findings serve as crucial support for upcoming studies concerning the realistic application of sludge-based biochar in the removal of antibiotics from water systems.

摘要

药品的广泛使用引起了人们对其在地表水中存在的日益关注。高浓度的磺胺甲恶唑(SMX)和林可霉素(LIN)作为常用的抗生素,存在于各种废水和地表水中,对公众健康和环境构成威胁。由易得的生物废物(如活性污泥生物量)制成的生物炭为减轻抗生素释放到水系统中提供了一种可持续和环保的解决方案。本研究调查了通过微波(MW)加热合成的 HPO 改性活性污泥基生物炭(PBC)对 SMX 和 LIN 抗生素的吸附效果。使用中心复合设计考虑 MW 功率、时间和 HPO 浓度优化了 PBC 的合成参数。表征结果验证了合成过程的有效性,产生了 365 m/g 的比表面积和发达的孔隙度,具有丰富的含氧官能团。进行了批量和动态吸附实验,以评估 PBC 在单一和二元抗生素系统中的吸附性能。结果表明,PBC 对 SMX 的亲和力高于 LIN,最大吸附容量分别为 45.6 mg/g 和 26.6 mg/g。基于动力学研究,化学吸附被认为是 SMX 和 LIN 去除的主要机制。平衡研究表明与 Redlich-Peterson 等温线吻合较好,表明两种抗生素的吸附机制更有可能是多层吸附。氢键和π-π电子共享被认为是 SMX 和 LIN 在改性生物炭上的主要吸附机制。此外,使用固定床柱装置复制了动态吸附系统,表明 PBC 负载水凝胶珠(PBC-B)可有效去除纯水和实际废水样品中的 SMX 和 LIN。这些发现为即将进行的研究提供了重要支持,即将研究污泥基生物炭在从水系统中去除抗生素方面的实际应用。

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