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FeCl3强化汞污染土壤热解吸修复
引用本文:何依琳,张 倩,许端平,马福俊,李发生,谷庆宝.FeCl3强化汞污染土壤热解吸修复[J].环境科学研究,2014,27(9):1074-1079.
作者姓名:何依琳  张 倩  许端平  马福俊  李发生  谷庆宝
作者单位:1.中国环境科学研究院, 环境基准与风险评估国家重点实验室, 北京 100012 ;辽宁工程技术大学环境科学与工程学院, 辽宁 阜新 123000
基金项目:国家高技术研究发展计划(863)项目(2013AA06A207)
摘    要:目前采用的热解吸技术修复汞污染土壤所需热解吸温度(600~800 ℃)较高,导致修复成本很高,也造成土壤本身结构的破坏. 采用在土壤中加入添加剂的方式来降低土壤修复的热解吸温度和热解吸时间, 分析了热解吸修复汞污染土壤时FeCl3的最佳投加量、热解吸时间和热解吸温度,并且对试验条件进行优化. 结果表明:在土壤中添加FeCl3能够有效提高汞的去除率,可降低热解吸所需的温度和时间. 当热解吸温度为400 ℃、热解吸时间为30 min时,随着c(FeCl3)/c(Hg)的增加,汞的去除率逐渐提高. c(FeCl3)/c(Hg)、热解吸温度、热解吸时间分别为150、450 ℃、20 min下,是汞污染土壤热解吸修复的最佳条件. 在热解吸过程中添加FeCl3,可以使土壤中的w(Hg)在较低热解吸温度、较短的热解吸时间下降至GB 15618—1995《土壤环境质量标准》三级标准限值(1.5 mg/kg)以下. 

关 键 词:FeCl3    热解吸        污染土壤
收稿时间:2013/9/26 0:00:00
修稿时间:2014/1/13 0:00:00

Thermal Desorption of Mercury from Contaminated Soil with the Addition of FeCl3 as Enhancement
HE Yi-lin,ZHANG Qian,XU Duan-ping,MA Fu-jun,LI Fa-sheng and GU Qing-bao.Thermal Desorption of Mercury from Contaminated Soil with the Addition of FeCl3 as Enhancement[J].Research of Environmental Sciences,2014,27(9):1074-1079.
Authors:HE Yi-lin  ZHANG Qian  XU Duan-ping  MA Fu-jun  LI Fa-sheng and GU Qing-bao
Institution:1.State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China ;College of Environmental Science and Engineering, Liaoning Technical University, Fuxin 123000, China2.State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China3.College of Environmental Science and Engineering, Liaoning Technical University, Fuxin 123000, China
Abstract:Current thermal desorption methods for remediating mercury contaminated soil are expensive and destructive to soil characteristics due to high treating temperatures (600-800 ℃). In the present study, relatively low temperature thermal desorption treatments with different additives for mercury contaminated soil were developed. The operating parameters including the amounts of additive, temperature and heating time were optimized. The results showed that high removal efficiency of mercury from soil could be obtained with FeCl3 as an additive during the thermal desorption process with a lower temperature and less time. The removal efficiency increased with increasing c(FeCl3)/c(Hg) when the soil was treated at 400 ℃ for 30 minutes. The addition of FeCl3 at 150 times the mole concentration of mercury in the soil was needed to effectively remove Hg from contaminated soils compared with no addition of FeCl3. The parameters were further optimized for thermal treatment at 450 ℃ for 20 minutes. With the addition of FeCl3, the mercury content in the contaminated soil could be reduced at relatively low temperature and short time to less than the limit of the environmental quality standard for soils of China. 
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