Bai Bing, Chen Jing, Zhang Bin
Key Laboratory of Urban Underground Engineering of Ministry of Education, Beijing Jiaotong University, Beijing, PR China.
Int J Phytoremediation. 2025;27(6):761-770. doi: 10.1080/15226514.2024.2443071. Epub 2024 Dec 22.
The flowing-water remediation of contaminated soil was investigated. Urease combined with biochar (UCB) technology was used to handle the Pb-contaminated sand column. The results showed that with the continuous increase of pore volume, the concentration of Pb in the leachate undergoes three stages: slow growth, rapid growth, and steady state. With increasing seepage velocity, the concentration of Pb in leachate increased slightly. The residual amount of each section of the sand column gradually decreased with increasing migration distance. The comparative results indicated that the UCB technology had a good solidification effect on Pb. This was due to urease-induced CaCO precipitation, cementation, and adsorption of Pb. Biochar provided more nucleation sites for urease, and some Pb was adsorbed on its surface or diffused into the pores of biochar, or ions exchanged with functional groups on the surface of biochar, which effectively stabilized the free Pb.
对污染土壤的流水修复进行了研究。采用脲酶结合生物炭(UCB)技术处理铅污染砂柱。结果表明,随着孔隙体积的不断增加,渗滤液中铅的浓度经历三个阶段:缓慢增长、快速增长和稳定状态。随着渗流速度的增加,渗滤液中铅的浓度略有增加。砂柱各段的残留量随迁移距离的增加而逐渐降低。对比结果表明,UCB技术对铅具有良好的固化效果。这是由于脲酶诱导碳酸钙沉淀、胶结以及铅的吸附作用。生物炭为脲酶提供了更多的成核位点,部分铅吸附在其表面或扩散到生物炭的孔隙中,或与生物炭表面的官能团发生离子交换,从而有效稳定了游离态的铅。