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使用生物炭、硫改性生物炭及其他有机改良剂减轻土壤中的镉污染。

Mitigating cadmium contamination in soil using Biochar, sulfur-modified Biochar, and other organic amendments.

作者信息

Huang Tianzhi

机构信息

Research Center of Rural Environmental Protection and Green Low-carbon Development, Mianyang Teachers College, Sichuan, China.

College of Engineering, Agriculture Aviation Innovation Lab, South China Agriculture University, Guangzhou, China.

出版信息

Int J Phytoremediation. 2025;27(6):874-887. doi: 10.1080/15226514.2025.2454515. Epub 2025 Jan 26.

DOI:10.1080/15226514.2025.2454515
PMID:39865581
Abstract

Biochar is a novel approach to remediating heavy metal-contaminated soil. Using various organic amendments like phyllosilicate-minerals (PSM), compost, biochar (BC) and sulfur-modified biochar (SMB), demonstrates superior adsorption capacity and stability compared to unmodified biochar (BC). The adsorption mechanisms of SMB are identified for its potential to increase soil-pH and reduce available cadmium (Cd). The study reveals the potential of BC and SMB in immobilizing Cd in contaminated soil. SMB demonstrated the highest adsorption capacity for Cd, followed by BC, PSM, and compost, with capacities ranging from 7.47 to 17.67 mg g. Both BC and SMB exhibit high adsorption capacities (12.82 and 17.67 mg g, respectively) and low desorption percentages (4.46-6.23%) at ion strengths of 0.01 to 0.1 mol-L and pH levels ranging from 5 to 7. SMB showed a higher adsorption capacity (17.67 mg g) and lower desorption percentage (4.46-6.23%) compared to BC. The adsorption mechanism involves surface-precipitation, ion exchange, and the formation of Cd(OH) and CdCO precipitates, as well as interactions between Cd and organic sulfur, leading to more stable-Cd and CdHS compounds. Adding 1% SMB increased soil pH and significantly reduced available Cd, demonstrating its potential for pollutant remediation. The study underscores the promise of SMB in providing a sustainable solution for Cd-contaminated soil remediation.

摘要

生物炭是一种修复重金属污染土壤的新方法。与未改性生物炭(BC)相比,使用各种有机改良剂,如层状硅酸盐矿物(PSM)、堆肥、生物炭(BC)和硫改性生物炭(SMB),具有更高的吸附能力和稳定性。SMB的吸附机制在于其具有提高土壤pH值和降低有效镉(Cd)的潜力。该研究揭示了BC和SMB在污染土壤中固定Cd的潜力。SMB对Cd的吸附能力最高,其次是BC、PSM和堆肥,吸附能力范围为7.47至17.67 mg/g。在离子强度为0.01至0.1 mol/L和pH值为5至7的条件下,BC和SMB均表现出高吸附能力(分别为12.82和17.67 mg/g)和解吸率低(4.46 - 6.23%)的特点。与BC相比,SMB表现出更高的吸附能力(17.67 mg/g)和解吸率更低(4.46 - 6.23%)。吸附机制包括表面沉淀、离子交换以及Cd(OH)和CdCO沉淀的形成,以及Cd与有机硫之间的相互作用,从而形成更稳定的Cd和CdHS化合物。添加1%的SMB可提高土壤pH值并显著降低有效Cd,证明了其在污染物修复方面的潜力。该研究强调了SMB在为Cd污染土壤修复提供可持续解决方案方面的前景。

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