ISSN 1000-3665 CN 11-2202/P

    活性硅铝原位反应带修复重金属污染地下水的试验研究

    Experimental study on remediation of heavy metal contaminated groundwater by in-situ reactive zone of active silica-aluminum

    • 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: The remediation of heavy metal-contaminated groundwater is often hindered by the limited mobility of conventional amendment materials, which restricts the formation of effective in situ reactive zones. Active silica-aluminum materials can not only fix heavy metals, but also migrate effectively in aquifers. To construct reaction zone in situ, an active silica-aluminum material was developed in the laboratory by physicochemical characterization, isothermal adsorption experiment, stability test, and column simulation experiment. 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 show that the active silica-aluminum has nanoscale pore size and amorphous morphology, with the surface zero charge point of approximately 1.7; the maximum adsorption capacities for Zn and Ni are 94.41, 2.40 mg/g, respectively. The fixation mechanism includes ion exchange and precipitation, and the medium of natural sand does not affect its fixation effect on heavy metals. The active silica-aluminum shows high stability, and the polymerization reaction increases with the decrease of pH and the extension of time, following the liquid-solid two phases migration mechanism. Column experiments show that Zn and Ni concentrations at the outlet rapidly decrease to below detection limits following injection, while treatment capacity increases over time. The hydraulic conductivity of the column initially decreases and then increased, with minimal net change. 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 decrease by more than 80% within 40 d. In engineering demonstration area, the migration and diffusion of active silica-aluminum is significant, and the immobilization effect was remarkable. Zn concentration decreases by more than 92.3% after 5 months, and the Zn concentration remains 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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