Inner Mongolia University of Science and Technology, School of Energy and Environment, Baotou, Inner Mongolia Autonomous Region 014010, China.
Inner Mongolia University of Science and Technology, School of Energy and Environment, Baotou, Inner Mongolia Autonomous Region 014010, China.
Sci Total Environ. 2020 Apr 1;711:135155. doi: 10.1016/j.scitotenv.2019.135155. Epub 2019 Nov 21.
The increasing production and use of silver nanoparticles (AgNPs) have attracted more and more attention due to their environmental and health risks. Municipal sewage biological treatment unit has been playing an important role in the removal of AgNPs. This study investigated the mechanism and characteristics of AgNPs and their removal from aqueous solution by activated sludge. Results from Scanning Electron Microscope and Energy Dispersive Spectrometer (SEM/EDS) showed that mixed AgNPs were immobilized by activated sludge. It was shown by X-ray photoelectron spectroscopy (XPS) that the fixed AgNPs had an oxidation state of +1. It was inferred by fourier transform infra-red (FTIR) spectra that AgNPs were adsorbed by activated sludge via binding with its primary amino (R-NH) radical groups on the surface. These results revealed that the major mechanism for the removal of AgNPs by activated sludge was adsorption. The experiment data were in agreement with the Langmuir and Redlich-Peterson isotherms. The maximum adsorption capacity ranged from 12-32 mg g at temperatures of 10-30 °C. Thermodynamic experiment showed that the adsorption of AgNPs by activated sludge was a spontaneous and endothermic reaction. The adsorption kinetics data were in good agreement with the pseudo-second-order model. The factor results indicated that the adsorption of AgNPs onto activated sludge was influenced by electrostatic repulsion, agglomeration, and the process of oxidation and sulfurization.
由于银纳米粒子(AgNPs)的环境和健康风险,其日益增加的生产和使用引起了越来越多的关注。城市污水生物处理单元在去除 AgNPs 方面发挥着重要作用。本研究考察了活性污泥对 AgNPs 及其从水溶液中去除的机制和特性。扫描电子显微镜和能谱仪(SEM/EDS)的结果表明,混合 AgNPs 被活性污泥固定。X 射线光电子能谱(XPS)表明,固定的 AgNPs 的氧化态为+1。傅里叶变换红外(FTIR)光谱表明,AgNPs 通过与表面上的初级氨基(R-NH)自由基结合被活性污泥吸附。这些结果表明,活性污泥去除 AgNPs 的主要机制是吸附。实验数据与 Langmuir 和 Redlich-Peterson 等温线一致。在 10-30°C 的温度下,最大吸附容量范围为 12-32 mg/g。热力学实验表明,AgNPs 被活性污泥吸附是一个自发的吸热反应。吸附动力学数据与准二级模型吻合较好。因子结果表明,AgNPs 被活性污泥吸附受到静电排斥、团聚以及氧化和硫化过程的影响。