Shandong Provincial Key Laboratory of Water Pollution Control and Resource Reuse, School of Environmental Science and Engineering, Shandong University, Jinan, Shandong 250100, China.
Shandong Provincial Key Laboratory of Water Pollution Control and Resource Reuse, School of Environmental Science and Engineering, Shandong University, Jinan, Shandong 250100, China.
Ecotoxicol Environ Saf. 2017 May;139:36-42. doi: 10.1016/j.ecoenv.2017.01.006.
Activated carbons were derived from Enteromorpha prolifera immersed in HPO solution or the HPO solution mixed with sodium benzenesulfonate (SBS), producing AC and AC-SBS. NaOH solution was employed in regeneration of ciprofloxacin (CIP)-loaded AC and AC-SBS to obtain RAC and RAC-SBS. The properties of the original and regenerated activated carbons were characterized by thermo-gravimetric analysis (TGA), scanning electron microscopy (SEM), N adsorption/desorption isotherms and Fourier transform infrared spectroscopy (FTIR). Batched adsorption studies were carried out to compare CIP adsorption behaviors of the four carbons. The results suggested that the four samples exhibited higher proportions of mesopores and similar functional groups. Although AC displayed much higher specific surface area (S) (1045.79m/g) than AC-SBS (738.03m/g), its CIP adsorption capacity was much less than AC-SBS. The maximum adsorption capacity for AC, AC-SBS, RAC and RAC-SBS were found to be 250mg/g, 286mg/g, 233mg/g and 256mg/g, respectively, with the isotherms adhering to Langmuir isotherm model. The electrostatic attraction and cation exchange between CIP and the four carbons were the dominant adsorption mechanisms. Moreover, the thermodynamic parameters represented that the adsorption process had been confirmed to be a spontaneous and endothermic reaction.
活性炭是由浸泡在 HPO 溶液或 HPO 溶液与苯磺酸钠(SBS)混合溶液中的浒苔衍生而来的,分别得到 AC 和 AC-SBS。NaOH 溶液用于再生载有环丙沙星(CIP)的 AC 和 AC-SBS,以获得 RAC 和 RAC-SBS。采用热重分析(TGA)、扫描电子显微镜(SEM)、N 吸附/解吸等温线和傅里叶变换红外光谱(FTIR)对原始和再生活性炭的性质进行了表征。进行了分批吸附研究,以比较四种碳对 CIP 的吸附行为。结果表明,四种样品均表现出较高比例的中孔和相似的官能团。尽管 AC 的比表面积(S)(1045.79m/g)明显高于 AC-SBS(738.03m/g),但其 CIP 吸附容量却远小于 AC-SBS。AC、AC-SBS、RAC 和 RAC-SBS 的最大吸附容量分别为 250mg/g、286mg/g、233mg/g 和 256mg/g,等温线符合朗缪尔等温线模型。CIP 与四种碳之间的静电吸引和阳离子交换是主要的吸附机制。此外,热力学参数表明,吸附过程是自发和吸热的。