Faculty of Earth Sciences, China University of Geosciences, Wuhan, China.
Colloids Surf B Biointerfaces. 2011 Nov 1;88(1):339-44. doi: 10.1016/j.colsurfb.2011.07.011. Epub 2011 Jul 12.
As one of the most important soil components, kaolinite plays a vital role in transport and retention of ionizable contaminants in soils of warm and wet climate. Ciprofloxacin (Cip) is a second generation fluoroquinolone (FQ) antibiotic of high use. It has high aqueous solubility under high and low pH conditions and higher stability in soil system. In this study, the interactions between Cip and kaolinite in aqueous solution were investigated by batch experiments, XRD and FTIR analyses. Quantitative correlation between the exchangeable cations desorbed and Cip adsorbed confirmed experimentally that cation exchange was the dominant mechanism of Cip adsorption on kaolinite. Fitting of experimental data to the cation exchange model resulted in a selectivity coefficient of 27, suggesting a strong affinity of Cip on negatively charged kaolinite surfaces. At the adsorption maximum 190-200 Å(2) was available per Cip molecule, much larger than the Cip molecule area, confirming charge-limited instead of surface-limited Cip adsorption. The invariable d-spacing after uptake of different amounts of Cip suggested that the adsorption of Cip was on the external surfaces of kaolinite. As solution pH increased beyond 8, the amount of Cip adsorption decreased significantly and reached close to zero at pH 11. The high adsorption rate constant due to surface adsorption instead of intercalation and the wide distribution of kaolinite in different soils suggest that the fate and transport of Cip may be governed by the transport of colloidal sized clays.
作为土壤的重要组成部分之一,高岭石在温暖湿润气候条件下土壤中可电离污染物的迁移和保持中起着至关重要的作用。环丙沙星(Cip)是一种高使用量的第二代氟喹诺酮(FQ)抗生素。它在高低 pH 值条件下具有高水溶性,在土壤系统中具有更高的稳定性。本研究通过批实验、XRD 和 FTIR 分析,研究了 Cip 在水溶液中与高岭石的相互作用。用解吸的可交换阳离子和吸附的 Cip 定量相关证实了实验阳离子交换是 Cip 吸附到高岭石上的主要机制。将实验数据拟合到阳离子交换模型得出的选择系数为 27,表明 Cip 对带负电荷的高岭石表面有很强的亲和力。在吸附最大值时,每个 Cip 分子可提供 190-200Å(2)的可用空间,远远大于 Cip 分子的面积,证实了电荷限制而不是表面限制的 Cip 吸附。在吸附不同量的 Cip 后不变的 d 间距表明 Cip 的吸附是在高岭石的外表面上进行的。随着溶液 pH 值超过 8,Cip 的吸附量显著下降,在 pH 值为 11 时接近零。由于表面吸附而不是插层,高吸附速率常数和高岭石在不同土壤中的广泛分布表明,Cip 的归趋和迁移可能受胶体大小粘土的迁移控制。