Zeng Hui-Ping, Yu Ya-Ping, Lü Sai-Sai, Li Dong, Zhang Jie
Key Laboratory of Beijing for Water Quality Science and Water Environment Recovery Engineering, Beijing University of Technology, Beijing 100124, China.
Beijing General Municipal Engineering Design & Research Institute Co., Ltd., Beijing 100082, China.
Huan Jing Ke Xue. 2019 Nov 8;40(11):5002-5008. doi: 10.13227/j.hjkx.201904232.
Backwashing sludge is an efficient adsorbent for arsenic removal. However, considering the practical application, it is unfavorable for solid-liquid separation. To overcome this disadvantage, a high-temperature baking method was used to prepare a granular adsorbent (GA) with iron-manganese sludge, along with an embedding method with drying (H-GA) and lyophilization (D-GA). The characterization results showed that the surface of the three adsorbents were rough, with specific surface areas of 43.830, 110.30, and 129.18 m·g, respectively. The adsorption experiments showed that the adsorption of arsenic by H-GA and D-GA was much higher than that of GA. The maximum adsorption capacities of GA, H-GA, and D-GA were 5.05, 14.95, and 13.45 mg·g, respectively. The Langmuir model fit the adsorption process of arsenic by H-GA and D-GA better, whereas the Freundlich model fit the adsorption process of GA better. The Pseudo-first order model and Pseudo-second order model were suitable to describe the kinetic curves of the three adsorbents. The acidic environment was more conducive to the adsorption of arsenic. The particle adsorbents prepared by the embedding method, H-GA and D-GA, retained the original structure of iron-manganese sludge, and the specific surface area was much larger than that of GA; thus, the adsorption capacity was greater than that of GA. Drying and lyophilization had no significant effect on the adsorption performance of granular adsorbents prepared by embedding.
反冲洗污泥是一种高效的除砷吸附剂。然而,考虑到实际应用,它不利于固液分离。为克服这一缺点,采用高温焙烧法用铁锰污泥制备颗粒吸附剂(GA),并采用干燥包埋法(H-GA)和冻干包埋法(D-GA)。表征结果表明,三种吸附剂表面粗糙,比表面积分别为43.830、110.30和129.18 m·g。吸附实验表明,H-GA和D-GA对砷的吸附量远高于GA。GA、H-GA和D-GA的最大吸附容量分别为5.05、14.95和13.45 mg·g。Langmuir模型更适合描述H-GA和D-GA对砷的吸附过程,而Freundlich模型更适合描述GA的吸附过程。准一级模型和准二级模型适合描述三种吸附剂的动力学曲线。酸性环境更有利于砷的吸附。采用包埋法制备的颗粒吸附剂H-GA和D-GA保留了铁锰污泥的原始结构,比表面积远大于GA,因此吸附容量大于GA。干燥和冻干对包埋法制备的颗粒吸附剂的吸附性能无显著影响。