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壳聚糖基复合材料负载废贻贝壳和废活性污泥炭对活性艳蓝 49 的吸附

Adsorption of reactive blue 49 onto cross-linked chitosan-based composites containing waste mussel shell and waste active sludge char.

机构信息

Department of Chemical Engineering, Faculty of Engineering, Pamukkale University, 20160 Denizli, Turkey.

Department of Chemical Engineering, Faculty of Engineering, Bilecik Seyh Edebali University, Bilecik, 11230 Turkey E-mail:

出版信息

Water Sci Technol. 2021 Feb;83(3):715-726. doi: 10.2166/wst.2021.008.

Abstract

Cross-linked chitosan/waste mussel shell (C/WMS) and chitosan/waste mussel shell/waste active sludge char (C/WMS/WASC) composites were prepared from waste mussel shell, waste active sludge (WAS), and chitosan, and cross-linked with glutaraldehyde. The quantities of chitosan, WMS, and WASC used for the C/WMS and C/WMS/WASC composites were 1:1 and 1:0.5:0.5, respectively. The two adsorbents were characterized for their quality by a scanning electron microscope (SEM), an energy-dispersive X-ray spectroscopy (EDX), and a Brunauer, Emmett and Teller (BET) analyzer. The effects of contact time (0-1,620 mins), pH (1-5), adsorbent dosage (0.01-0.1 g/50 ml), initial dye concentration (20-100 mg/L), and temperature (25-45 °C) on Reactive Blue 49 (RB49) adsorption onto C/WMS and C/WMS/WASC composites were investigated. The maximum RB49 adsorption capacity of C/WMS and C/WMS/WASC composites was 54.7 and 38.8 mg/g, respectively. The experimental data were analyzed by kinetic and isotherm models. The Freundlich isotherm was a good fit for the experimental data of RB49 adsorption on C/WMS and C/WMS/WASC composites, and the adsorption kinetics for both adsorbents were the pseudo-second-order rate equation. All results showed the preparative adsorbents can be used as effective adsorbents for the treatment of waste water contaminated with RB49 since they are low cost and eco-friendly for the environment.

摘要

交联壳聚糖/废贻贝壳(C/WMS)和壳聚糖/废贻贝壳/废活性污泥炭(C/WMS/WASC)复合材料由废贻贝壳、废活性污泥(WAS)和壳聚糖制备,并与戊二醛交联。用于 C/WMS 和 C/WMS/WASC 复合材料的壳聚糖、WMS 和 WASC 的量分别为 1:1 和 1:0.5:0.5。通过扫描电子显微镜(SEM)、能谱(EDX)和 Brunauer、Emmett 和 Teller(BET)分析仪对两种吸附剂的质量进行了表征。考察了接触时间(0-1,620 分钟)、pH 值(1-5)、吸附剂用量(0.01-0.1 g/50 ml)、初始染料浓度(20-100 mg/L)和温度(25-45°C)对 C/WMS 和 C/WMS/WASC 复合材料吸附活性蓝 49(RB49)的影响。C/WMS 和 C/WMS/WASC 复合材料对 RB49 的最大吸附容量分别为 54.7 和 38.8 mg/g。实验数据通过动力学和等温线模型进行了分析。Freundlich 等温线很好地拟合了 RB49 在 C/WMS 和 C/WMS/WASC 复合材料上的吸附实验数据,两种吸附剂的吸附动力学均符合准二级速率方程。所有结果表明,由于制备的吸附剂成本低且对环境友好,因此可作为处理 RB49 污染废水的有效吸附剂。

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