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热脱附-稳定化工序对土壤镉稳定化效率的影响
引用本文:牛明芬,陈驰,吴波,郭书海,李刚,徐丽,闫晓峰.热脱附-稳定化工序对土壤镉稳定化效率的影响[J].环境工程,2023,41(2):166-172.
作者姓名:牛明芬  陈驰  吴波  郭书海  李刚  徐丽  闫晓峰
作者单位:1. 沈阳建筑大学 市政与环境工程学院, 沈阳 110168;
基金项目:国家重点研发计划课题"东北遗留场地重金属污染防治与安全利用技术体系构建"(2020YFC1806404)
摘    要:热脱附-稳定化是修复重金属-有机物复合污染土壤的主要工艺。由于热脱附对土壤重金属有“活化”和“固化”的双重作用,因此,热脱附-稳定化工序会影响重金属的稳定化效率。以含镉(Cd)的复合污染土壤为研究对象,从浸出率、形态分布、微观形貌3个层面,分析热脱附-稳定化(T-S)和稳定化-热脱附(S-T)工艺对Cd稳定化效率的影响。结果表明:S-T工艺浸出率(42.26%)低于T-S工艺(52.11%);由于Cd“活化”“固化”与稳定化作用,S-T工艺处置的土壤Cd弱酸提取态和残渣态比例分别是T-S工艺的0.75,1.4倍,形态更趋于稳定分布;电镜扫描(SEM)显示,S-T工艺比T-S工艺处置后土壤颗粒结晶更为显著,说明土壤Cd的稳定化效果更好。

关 键 词:热脱附  稳定化  工艺顺序  稳定化效率  浸出率  形态分布  电镜扫描
收稿时间:2021-12-26

INFLUENCE OF SEQUENCE OF THERMAL DESORPTION-STABILIZATION ON SOIL CADMIUM STABILIZATION EFFICIENCY
Affiliation:1. School of Municipal and Environmental Engineering, Shenyang Jianzhu University, Shenyang 110168, China;2. Shenyang Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110016, China;3. National-Local Joint Engineering Laboratory of Contaminated Soil Remediation by Bio-Physicochemical Synergistic Process, Shenyang 110016, China;4. Huludao Ecological Environment Service Center, Huludao 125000, China
Abstract:Thermal desorption-stabilization was the main process for repairing heavy metal-organic co-contaminated soil. Thermal desorption had the dual effect of "activation" and "solidification" on heavy metals in the soil, so the thermal desorption-stabilization sequences will affect the stabilization efficiency of heavy metals. In this study, the co-contaminated soil containing cadmium (Cd) was used as the research object to analyze the effect of thermal desorption-stabilization (T-S) and stabilization-thermal desorption (S-T) processes on Cd stabilization efficiency, from the three levels of leaching rate, morphological distribution, and micromorphology. The results showed that the leaching rate of S-T process (42.26%) was lower than that of T-S process (52.11%). Due to the activation, solidification and stabilization effect of Cd, the ratio of weak acid extraction and residue of soil Cd treated by S-T process was 0.75 and 1.4 times that of T-S process, and the morphological distribution of Cd in the soil tended to be more stable. Scanning electron microscope (SEM) showed that S-T process had more significant soil particle crystallization than T-S process, which characterizes that Cd stabilization was better.
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