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摘要:
渗透系数是评价重金属污染液在重塑黄土中迁移扩散作用的一个重要指标。已有研究表明污染液的pH值、可溶性盐浓度、离子含量和饱和渗透系数的变化存在一定的相关关系,但未明晰渗透过程中的地球化学反应机制。基于此,采集了西安白鹿原地区的更新统(Qp)黄土,选取Cu2+溶液作为渗透溶液,开展了重塑黄土的饱和渗透试验,建立了基于Netpath软件的地球化学反演模型。结果表明:试验过程中饱和渗透系数从第1天开始显著降低,且与去离子试验组相比降低幅度较大,极差为5.57×10−5 cm/s;离子来源分析证明了地球化学反应的发生,存在着矿物的溶解、沉淀以及阳离子交换作用;地球化学反演模拟结果显示由于Cu2+的存在,加剧了矿物溶解产生大量的Ca2+,促进碳酸盐矿物溶解平衡左移,从第1天开始方解石和白云石持续形成沉淀,沉淀量分别为1.912,0.958 mmol,从而堵塞渗流孔隙,降低土体的渗透系数。研究结果有助于了解重金属离子侵入过程中重塑黄土饱和渗透系数的变化,同时对于进一步明晰影响渗透系数变化的地球化学机制具有重要的理论意义。
Abstract:The coefficient of permeability is an important index to evaluate the migration and diffusion of heavy metal polluted liquid in remodeled loess. At present, the existing studies have shown that there is a certain correlation among the pH value, the value of electrical conductivity, ion content and saturated coefficient of permeability of the polluted liquid, but the geochemical reaction mechanism during the infiltration process has not been clarified. Therefore, the Qp loess in the Bailuyuan area of Xi’an is collected, and the Cu2+ solution is selected as the infiltration solution to carry out the saturated infiltration test of the reshaped loess, and the geochemical inversion model based on the Netpath software is established. The results show that the saturated coefficient of permeability decreases significantly from the first day during the test, and has a larger decrease compared with the deionized test group, with a range of 5.57×10−5 cm/s. The ion source analysis proves that the geochemical reaction occurs, including mineral dissolution, precipitation and cation exchange. The geochemical inversion simulation results show that the presence of Cu2+ aggravates the mineral dissolution and produces a large amount of Ca2+, which promotes the leftward shift of the carbonate mineral dissolution balance, starting from the first day continual calcite and dolomite precipitation, and the precipitation amounts are 1.912 mmol and 0.958 mmol, respectively, which blocked the seepage pores and reduced the coefficient of permeability of the soil. The results are helpful in understanding the change of the saturated the permeability coefficient of the remodeled loess during the intrusion of heavy metal ions, and are of important theoretical significance for further clarifying the geochemical mechanism affecting the change of the permeability coefficient.
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Key words:
- remolded loess /
- heavy mental pollution /
- saturated permeability /
- geochemistry
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表 1 土样的物理性质
Table 1. Physical properties of the soil sample
参数 最优含水率
/%最大干密度
/(g·cm−3)比重 液限/% 塑限/% 粒度分布/% 粉粒 黏粒 砂粒 取值 17.78 1.76 2.6 39.47 19.73 21.32 78.38 0.30 表 2 土样的主要化学成分
Table 2. Main chemical components of the soil sample
化学成分 SiO2 Al2O3 Fe2O3 MgO CaO Na2O K2O 其他 质量分数/% 62.15 1.74 12.95 1.96 5.65 2.41 4.89 8.25 表 3 饱和渗透系数的极差和平均值
Table 3. Range and average value of the saturated coefficient of permeability
溶液类型 最大值/(cm·s−1) 最小值/(cm·s−1) 极差/(cm·s−1) DIW 7.37×10−5 4.97×10−5 2.40×10−5 Cu2+溶液 6.66×10−5 1.09×10−5 5.57×10−5 表 4 矿物饱和指数(SI)
Table 4. Mineral saturation index (SI)
离子类型 渗透时间/d 矿物相 方解石 白云石 萤石 石膏 岩盐 DIW 0.5 −0.43 −1.44 −0.63 −2.58 −7.14 1.0 −0.71 −1.94 −0.56 −3.13 −7.32 1.5 −0.96 −2.50 −0.40 −3.27 −7.47 2.0 −0.99 −2.57 −0.81 −3.29 −7.79 2.5 −0.50 −3.50 −1.33 −3.24 −8.19 3.0 −0.16 −2.87 −1.45 −3.07 −8.67 3.5 0.05 −2.56 −1.58 −3.04 −9.15 4.0 0.23 −2.73 −1.52 −2.87 −9.42 4.5 0.18 −2.15 −1.50 −2.76 −9.47 5.0 0.09 −2.81 −1.63 −2.89 −9.91 Cu2+ 0.5 −0.22 −1.00 −0.68 −1.06 −6.79 1.0 0.26 0.03 −0.76 −1.83 −7.69 1.5 0.39 0.27 −0.78 −1.88 −8.85 2.0 0.34 0.06 −0.93 −1.88 −9.20 2.5 0.41 0.08 −0.95 −1.87 −9.47 3.0 0.12 −0.57 −1.05 −1.86 −9.58 3.5 0.55 0.23 −1.19 −1.86 −9.64 4.0 0.62 0.35 −1.16 −1.86 −9.62 4.5 0.55 0.2 −1.18 −1.85 −9.71 5.0 0.48 0.04 −1.39 −1.87 −9.66 表 5 潜在的化学反应
Table 5. Potential chemical reactions
序号 反应相 化学反应 1 方解石 CaCO3=Ca2++CO32− 2 白云石 CaMg(CO3)=Ca2++Mg2++CO32− 3 萤石 CaF2=Ca2++2F− 4 石膏 CaSO4·2H2O=Ca2++SO42−+2H2O 5 钾长石 KAlSi3O8+8H2O=K++Al(OH)4−+3H4SiO4 6 伊利石 K0.6Mg0.25Al2.3Si3.5O10(OH)2+11.2H2O=
0.6K++0.25Mg2++2.3Al(OH)4−+3.5H4SiO4+1.2H+7 岩盐 NaCl=Na++Cl− 8 离子交换 Ca2++2NaX=2Na++CaX2 -
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