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Enhanced removal efficiency of Cd2+ and Pb2+ from aqueous solution by H3PO4–modified tea branch biochar: Characterization, adsorption performance and mechanism

生物炭 水溶液 吸附 吸热过程 化学 朗缪尔吸附模型 朗缪尔 无机化学 核化学 有机化学 热解
作者
Haojie Xu,Qi Zhou,Tengyu Yan,Xiangwei Jia,Dandan Lu,Yanfang Ren,Junyu He
出处
期刊:Journal of environmental chemical engineering [Elsevier]
卷期号:12 (2): 112183-112183 被引量:11
标识
DOI:10.1016/j.jece.2024.112183
摘要

Biochar has been widely recognized as an environmentally efficient adsorbent for removal of heavy metals in wastewater. However, inferior adsorption capacity limits its practical application. In this study, a H3PO4–modified tea branch biochar (PTBB) was firstly prepared through the one step pyrolysis of H3PO4-pretreated tea branch powder for enhancing removal efficiency of Cd2+ and Pb2+ from aqueous solutions. H3PO4 modification altered the physicochemical properties of pristine biochar. The PTBB exhibited superior adsorption performance. Its maximum adsorption capacities of Cd2+ and Pb2+ were 98.25 mg g−1 and 127.5 mg g−1 at the pH 6 and dosage of 2 g L−1, which was 1.5 and 1.3 folds of the pristine biochar, respectively. Cd2+ and Pb2+ adsorption data by PTBB were well fitted by the Langmuir isothermal and pseudo-second order kinetic models, indicating monolayer chemical adsorption controlled the adsorption process. The adsorption of Cd2+ and Pb2+ by PTBB was a spontaneous endothermic process and less affected by coexisting cations. PTBB demonstrated a greater affinity for Pb2+ as compared with Cd2+ in binary metal systems. Moreover, PTBB could maintain good stability and regeneration properties. The adsorption of Cd2+ and Pb2+ by PTBB was attributed to cation exchange, precipitation, complexation, and π electron interactions. The quantitative analysis indicated that complexation and precipitation were the primary adsorption mechanisms, which accounted for 50.52–50.56% and 36.7–42.18% to total Cd2+ and Pb2+ adsorption for PTBB, respectively. Therefore, PTBB exhibits great potential for application in the remediation of wastewater containing Cd2+ or Pb2+.
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