School of Energy and Environmental Engineering, University of Science and Technology Beijing, Beijing 100083, China; Beijing Key Laboratory on Resource-oriented Treatment of industrial Pollutants, Beijing 100083, China.
School of Energy and Environmental Engineering, University of Science and Technology Beijing, Beijing 100083, China; Beijing Key Laboratory on Resource-oriented Treatment of industrial Pollutants, Beijing 100083, China.
Sci Total Environ. 2020 May 15;717:137014. doi: 10.1016/j.scitotenv.2020.137014. Epub 2020 Jan 30.
Biochar plays a significant role in soil remediation. However, the simultaneous immobilization mechanism and relationship of biochar to cations and anions have never been clear. We designed a batch incubation experiment to investigate the impact of corncob-based biochars to cadmium (Cd) and arsenic (As) contaminations in yellow soil and cinnamon soil, and analyze the relationships among biochars physicochemical characteristics (surface area: SA, total pore volume: TV, average pore size: AV and the C/O rate), soil properties, metals immobilization and microbial diversity indices. Results showed that the modified biochars (inorganic-modified biochar: BCTD) had a good effect on heavy metals immobilization and transformed acid extractable and reducible fraction into the residual fraction. Total nitrogen, organic matter and available potassium increased in both soils after biochar application. The principal component analysis presented that the smaller C/O rate was favorable to As stabilization; the SA and TV of biochar were negatively correlated with the leaching concentration of Cd. The larger surface area, higher porosity and organic matters of biochar were more beneficial to soil microbial diversity. This work not only can demonstrate remediation mechanisms of heavy metals contaminated soil by biochars, but also gain an application of biochars technology in the recycling and reutilize of agricultural waste, and provide a clear strategy for heavy metals contaminated soil, especially As and Cd.
生物炭在土壤修复中起着重要作用。然而,生物炭对阳离子和阴离子的同时固定机制及其关系尚不清楚。我们设计了一个批式培养实验,以研究玉米芯基生物炭对黄壤和肉桂土中镉(Cd)和砷(As)污染的影响,并分析生物炭物理化学特性(比表面积:SA、总孔体积:TV、平均孔径:AV 和 C/O 率)、土壤性质、金属固定化和微生物多样性指数之间的关系。结果表明,改性生物炭(无机改性生物炭:BCTD)对重金属固定化效果较好,将酸可提取态和可还原态转化为残渣态。施入生物炭后,两种土壤中的全氮、有机质和速效钾均增加。主成分分析表明,较小的 C/O 率有利于 As 的稳定;生物炭的 SA 和 TV 与 Cd 的浸出浓度呈负相关。生物炭较大的比表面积、较高的孔隙率和有机质更有利于土壤微生物多样性。这项工作不仅可以证明生物炭对重金属污染土壤的修复机制,还可以为农业废弃物的回收和再利用提供生物炭技术的应用,并为重金属污染土壤,特别是 As 和 Cd 提供明确的策略。