Key Laboratory of Original Environmental Pollution Prevention and Control, Ministry of Agriculture and Rural Affairs, Tianjin 300191, China.
Tianjin Key Laboratory of Agro-Environment and Agro-Products, Agro-Environmental Protection Institute, Ministry of Agriculture and Rural Affairs, Tianjin 300191, China.
Int J Environ Res Public Health. 2022 Jan 23;19(3):1260. doi: 10.3390/ijerph19031260.
In order to develop a low-cost, fast, and efficient adsorbent, the fish bone charcoal B prepared at 600 °C was modified by chitosan (Cs) and FeO to produce the material Cs-FeO-B. Results showed that Cs-FeO-B had magnetic responsiveness and can achieve solid-liquid separation, macropores disappeared, pore volume and specific surface area are increased, and amino functional groups appear on the surface. The adsorption process of Cd(II) by Cs-FeO-B conformed best to the pseudo-second order kinetics model and the Langmuir model, respectively. The behavior over a whole range of adsorption was consistent with chemical adsorption being the rate-controlling step, which is a very fast adsorption process, and the isothermal adsorption is mainly monolayer adsorption, which belongs to favorable adsorption. In addition, the saturated adsorption capacity obtained for the Cs-FeO-B to Cd(II) was 64.31 mg·g, which was 1.7 times than B. The structure and morphology of Cs-FeO-B were characterized through SEM-EDS, TEM, FTIR, and XRD, indicating that the main mechanism of Cs-FeO-B and Cd(II) is mainly the complexation of amino groups, and it also includes part of the ion exchange between Cd(II) and FeO. Therefore, Cs-FeO-B can be employed as an effective agent for remediation of Cd contaminated water.
为了开发一种低成本、快速、高效的吸附剂,将在 600°C 下制备的鱼骨炭 B 通过壳聚糖(Cs)和 FeO 进行改性,得到 Cs-FeO-B 材料。结果表明,Cs-FeO-B 具有磁响应性,可以实现固液分离,大孔消失,孔体积和比表面积增加,表面出现氨基官能团。Cs-FeO-B 对 Cd(II)的吸附过程分别最好地符合伪二级动力学模型和 Langmuir 模型。整个吸附范围内的行为与化学吸附一致,化学吸附是控制步骤,这是一个非常快速的吸附过程,等温吸附主要是单层吸附,属于有利吸附。此外,Cs-FeO-B 对 Cd(II)的饱和吸附容量为 64.31 mg·g,是 B 的 1.7 倍。通过 SEM-EDS、TEM、FTIR 和 XRD 对 Cs-FeO-B 的结构和形态进行了表征,表明 Cs-FeO-B 和 Cd(II)的主要作用机制主要是氨基的络合作用,同时也包括 Cd(II)与 FeO 之间部分的离子交换。因此,Cs-FeO-B 可作为一种有效修复 Cd 污染水的试剂。