Nano-Biopolymers Research Laboratory, School of Chemical Engineering, College of Engineering, University of Tehran, P. O. Box, 11155-4563, Tehran, Iran.
Nano-Biopolymers Research Laboratory, School of Chemical Engineering, College of Engineering, University of Tehran, P. O. Box, 11155-4563, Tehran, Iran.
J Environ Manage. 2019 May 15;238:166-177. doi: 10.1016/j.jenvman.2019.02.124. Epub 2019 Mar 6.
This work aimed at producing nanoparticles (NPs) based on thiol-functionalized chitosan (CS) using capillary microfluidic (MF) device combined with ionic gelation method to adsorb mercury ion [Hg (II)] from aqueous solutions. In this line, CS was functionalized with epichlorohydrin/cysteaminium chloride (2.73 M ratio) followed by fabricating NPs via MF and bulk mixing (BM) methods. To characterize the morphology, zeta potential, functionality, structure, and magnetic property of the samples, a series of tests such as SEM, TEM, DLS, FTIR, XRD, and VSM were carried out, respectively. The obtained results showed that MF technique was able to produce NPs with a diameter as small as 18 ± 3 nm, and a uniform shape compared to BM method. Thiol groups (-SH) functionalization on CS surface was confirmed by appearing a characteristic peak at 2579 cm. Also, the XRD patterns indicated the appropriate synthesis of FeO (magnetite), and no change in the structure of CS NPs in the presence of magnetite. Moreover, adding the magnetite to thiol-functionalized CS NPs led to suitable saturation magnetization about 26 emu/g to facilitate their separation using a magnetic field. To evaluate the performance of the nanoadsorbent, it has been exposed to Hg (II) in an aqueous solution which in turn the parameters optimization for the adsorption was done via Box-Behnken design (BBD) method, exhibiting the effect of adsorbent dose and the initial concentration of Hg (II) was much more significant than that of pH. Different concentrations of total dissolved solids up to 1000 mg/L had no adverse impact on the adsorption process confirmed by EDAX spectra. The least value of RMSE (5.023) and χ (0.3) were observed for Redlich-Peterson, Radke-Prausnitz, and UT isotherms. Maximum adsorption capacities calculated using Langmuir and UT models were 1192 mg/g and 1126 mg/g, respectively. Thermodynamic studies demonstrated that the nature of the adsorption process was spontaneous and endothermic. Recovery of nanoadsorbent was successfully carried out using HCl 0.5 mol/L. The adsorption studies revealed that the prepared nanoadsorbent is promising candidate used in mercury removal from a real wastewater potentially.
本工作旨在使用基于巯基功能化壳聚糖 (CS) 的纳米粒子 (NPs),通过毛细管微流控 (MF) 装置结合离子凝胶化法从水溶液中吸附汞离子 [Hg (II)]。为此,CS 用表氯醇/半胱胺盐酸盐 (2.73 M 比) 进行功能化,然后通过 MF 和体混合 (BM) 方法制备 NPs。为了表征样品的形态、zeta 电位、功能、结构和磁性,分别进行了一系列测试,如 SEM、TEM、DLS、FTIR、XRD 和 VSM。结果表明,MF 技术能够制备出直径仅为 18 ± 3 nm 的 NPs,且形状比 BM 法更均匀。CS 表面巯基 (-SH) 功能化通过在 2579 cm 处出现特征峰得到证实。此外,XRD 图谱表明,在存在磁铁矿的情况下,适当合成了 FeO (磁铁矿),且 CS NPs 的结构没有变化。此外,将磁铁矿添加到巯基功能化的 CS NPs 中,可获得约 26 emu/g 的合适饱和磁化强度,以便使用磁场方便地分离它们。为了评估纳米吸附剂的性能,将其暴露于水溶液中的 Hg (II) 中,然后通过 Box-Behnken 设计 (BBD) 方法对吸附进行参数优化,结果表明吸附剂剂量和 Hg (II) 的初始浓度的影响比 pH 值更为显著。通过 EDAX 光谱证实,高达 1000 mg/L 的总溶解固体浓度对吸附过程没有不利影响。对于 Redlich-Peterson、Radke-Prausnitz 和 UT 等模型,RMSE (5.023) 和 χ (0.3) 的最小值观察到为 Redlich-Peterson、Radke-Prausnitz 和 UT 模型。使用 Langmuir 和 UT 模型计算得到的最大吸附容量分别为 1192 mg/g 和 1126 mg/g。热力学研究表明,吸附过程的性质是自发的和吸热的。使用 0.5 mol/L HCl 成功回收了纳米吸附剂。吸附研究表明,制备的纳米吸附剂是从实际废水中去除汞的有前途的候选物。