Synergistic enhanced passivation of phosphorus and cadmium in sediment by Ca/Al co-modified biochar

化学 吸附 磷酸盐 生物炭 氢氧化物 金属 核化学 无机化学 环境化学 有机化学 热解
作者
Fengrui Zhang,Lianzhou Wang,Yifan Wang,Yanmin Cao,Shenghua Zhang
出处
期刊:Chemical Engineering Journal [Elsevier BV]
卷期号:474: 145539-145539 被引量:7
标识
DOI:10.1016/j.cej.2023.145539
摘要

Currently, lakes are facing increasingly severe combined pollution from eutrophication and heavy metals. A novel material was prepared by modification peanut shell biochar with calcium (Ca)-aluminum (Al) (CA@BC) in this study. Its maximum adsorption capacity (Qmax) reached 97.9 and 88.7 mg/g for phosphorus (P) and cadmium (Cd), respectively, and it showed synergistic enhancement during synchronous adsorption. Not entirely consistent with the adsorption mechanisms for P or Cd alone, the phosphate precipitation and inner sphere complexes (the coordination bonds formation between carbon and metal with phosphate, C/Al/Cd–O–P) were accounted for P adsorption by CA@BC during synchronous adsorption. And the Cd removal was caused by the formation of phosphate and hydroxide precipitates, as well as a small amount of Cd–O–P and Cd–O–C inner sphere complexes. The sediment results of individual P and simultaneous P and Cd indicated that the CA@BC capping had a good immobilization effect on sediment P and Cd, especially in alleviating their increased release intensity caused by anoxic conditions, and helped to maintain consistently low P and Cd concentrations in the overlying water. Both active P and Cd in surface sediments could be converted to their stable states by the capping of CA@BC, in which iron bound P (Fe–P) and the weak acid extractable Cd and reducible Cd were primarily transformed to Ca bound P (Ca–P) and residual Cd, respectively. In addition, CA@BC has a stronger transformation effect on the active Fe–P in surface sediments during simultaneous passivation. Therefore, CA@BC showed a great potential in the passivation of sediment P and Cd, and provided a good solution for the remediation of eutrophic heavy metal-contaminated sediments.
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