ISSN 1000-3665 CN 11-2202/P

    构建活性硅铝原位反应带修复重金属污染的地下水:从实验研究到场地尺度示范

    Construction of active silica-aluminum in-situ reaction zone for remediation of heavy metal contaminated groundwater—from experimental research to site scale demonstration

    • 摘要: 对于场地地下水重金属污染问题,当前的纳米零价铁等材料迁移性较差,注入后难以形成修复反应带,而活性硅铝材料除可固定重金属外,还可在含水层中有效迁移。为原位构建活性硅铝反应带,在实验室内采用理化性质表征、等温吸附试验、稳定性测试、柱模拟试验等方法研发活性硅铝修复材料,并选取某有色金属矿区尾矿库下游含重金属Zn、Ni的地下水历史渗漏区开展场地尺度中试试验与工程示范。研究结果表明:(1)活性硅铝材料具有纳米级孔径和无定形态,表面零电荷点为1.7左右;对Zn和Ni复合污染水体的最大吸附量分别为94.41 mg/g和2.40 mg/g,固定作用包含离子交换和沉淀等多种机理,天然砂介质不会影响其对重金属的固定效果;活性硅铝稳定性良好,聚合反应随体系pH降低和时间延长而增强,遵循液固双相迁移机制。(2)注入模拟砂柱后,可使注入口Zn和Ni浓度迅速降低至未检出,出口处对重金属的处理能力继续增强,模拟砂柱渗透系数先减小后增大,总体变化不大。(3)将其以注入方式构建原位反应带修复场地地下水中重金属,中试区Zn和Ni浓度在40 d内降低80%以上,工程示范区活性硅铝迁移扩散明显,修复效果良好,Zn浓度降低92.3%以上,经过5个月的监测,Zn浓度维持在地下水Ⅲ类标准值以下。注入活性硅铝可有效构建原位反应带修复重金属污染的地下水。

       

      Abstract: For the problem of heavy metal pollution in groundwater, the current remediation materials have poor mobility, and it is difficult to form effective reaction zones after injection. Active silica-aluminum materials can not only fix heavy metals, but also migrate effectively in aquifers. In order to construct reaction zone in situ, an active silica-aluminum material was developed in the laboratory by means of physicochemical characterization, isothermal adsorption experiment, stability test, column simulation experiment, etc. In addition, site-scale pilot test and engineering demonstration were carried out in the historical leakage area of groundwater contaminated by Zn and Ni at downstream of the tailings pond of a non-ferrous metal mining area. The results showed: (1) The active silica-aluminum had nanoscale pore size and amorphous morphology, and the surface zero charge point was about 1.7; the maximum adsorption capacities for Zn and Ni were 94.41 mg/g and 2.40 mg/g respectively, the fixation mechanism included ion exchange, precipitation and so on, and the medium of natural sand did not affect its fixation effect on heavy metals; the stability of active silica-aluminum was very well, the polymerization reaction increased with the decrease of pH and the extension of time, and active silica-aluminum followed the liquid-solid two phases migration mechanism. (2) After injected in the simulated sand column, the concentrations of Zn and Ni at the sprue reduced to undetected rapidly, and the treatment capacity of heavy metals at the exit continued to increase. The permeability coefficient of the simulated sand column first decreased and then increased, with little overall change. (3) In-situ reaction zone was constructed by injecting active silica-aluminum to immobilize heavy metals in groundwater of the site. The concentrations of Zn and Ni in the pilot area decreased by more than 80% within 40 d. In engineering demonstration area, the migration and diffusion of active silica-aluminum was obvious and immobilization effect was remarkable, Zn concentration decreased by more than 92.3%, after 5 months of monitoring, the Zn concentration remained below the standard value of groundwater III. Injecting active silica-aluminum can effectively construct in-situ reaction zone to remediate groundwater contaminated by heavy metals.

       

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