Département de Chimie Inorganique, Laboratoire de Chimie Physique et Analytique Appliquée, Université de Yaoundé I, P.O.Box: 812, Yaoundé, Cameroon.
School of geology and mining engineering, University of Ngaoundere, P.O.Box: 454, Ngaoundere, Cameroon.
Environ Sci Pollut Res Int. 2020 Jun;27(16):20500-20515. doi: 10.1007/s11356-020-08536-3. Epub 2020 Apr 3.
The reason that some molecules, but not others, are easily adsorbed was not fully understood. In order to spotlight the effect of morphological structure and surface functional composition of adsorbate rather than focusing only on the nature of adsorbent as in most of literature reports, this work reports the biosorption of two dyes (anionic Orange G and cationic malachite green) and two pharmaceuticals (Ibuprofen and ampicillin) as target representative contaminants onto plasma-modified cocoa shell (CPHP) used as alternative low-cost adsorbent. As results, when molecules were mixed in solution and then exposed to a substrate, the factors that affect adsorption include the relative solvation of the adsorbates, the ability of each molecule to adhere to the surface, and the degree of interaction between the molecules once they were adsorbed. The maximum adsorbed amounts at 298 K of OG, MG, IBP, and AMP were 23.96, 14.65, 13.99, and 06.66 mg/g, respectively. The most solvated molecules may not adsorb rapidly to the surface, while comparatively, the less soluble molecules will aggregate, so as to maximize self-interactions via Van der Waals, hydrogen bonds or other interactions. This work demonstrated that the adsorbate intrinsic properties could play a significant role in the adsorption process. Hence, properties such as functional active groups, dimensions, and hydrophobicity were the determining parameters in the adsorption process mechanism. Accordingly, the pharmaceuticals biosorption mechanism involved π-π bonding, hydrophobic effect, electrostatic interaction, and van der Waals forces whereas the dye biosorption mechanism was dominated as well known by electrostatic attraction and hydrogen bonding phenomenon. Experimental parameters such as initial pH of solution and contact time were optimized. The optimum pH values were 2.0 for ibuprofen (IBP) and 7.0 for ampicillin (AMP). The kinetics of adsorption and the experimental isotherms data were analyzed using non-linear models. Results indicated that Avrami fractional order was the most successfully fitted model for pharmaceutical biosorption and based on the statistical values of SD and R parameters, Liu isotherm was the most successfully fitted model.
有些分子很容易被吸附,而有些则不然,其原因尚未完全明了。为了突出吸附物的形态结构和表面官能团组成的影响,而不是像大多数文献报道那样只关注吸附剂的性质,本工作报道了两种染料(阴离子橙 G 和阳离子孔雀绿)和两种药物(布洛芬和氨苄西林)作为目标代表性污染物在等离子体改性可可壳(CPHP)上的生物吸附,CPHP 用作替代的低成本吸附剂。结果表明,当分子在溶液中混合然后暴露在基质上时,影响吸附的因素包括吸附物的相对溶剂化作用、每个分子粘附在表面的能力以及分子一旦被吸附后的相互作用程度。在 298 K 时,OG、MG、IBP 和 AMP 的最大吸附量分别为 23.96、14.65、13.99 和 06.66 mg/g。最溶剂化的分子可能不会迅速吸附到表面,而相对地,溶解度较低的分子会聚集,从而通过范德华力、氢键或其他相互作用最大化自身相互作用。本工作表明,吸附物的固有性质在吸附过程中可能起重要作用。因此,如官能团、尺寸和疏水性等性质是吸附过程机制中的决定参数。因此,药物的生物吸附机制涉及π-π键合、疏水作用、静电相互作用和范德华力,而染料的生物吸附机制则主要由静电吸引和氢键现象决定。优化了初始溶液 pH 值和接触时间等实验参数。布洛芬(IBP)的最佳 pH 值为 2.0,氨苄西林(AMP)的最佳 pH 值为 7.0。采用非线性模型分析了吸附动力学和实验等温线数据。结果表明,阿弗拉米分数阶模型最适合药物生物吸附,基于 SD 和 R 参数的统计值,刘等温线是最适合的模型。