Spalding B P, Spalding I R
Environmental Sciences Division, Oak Ridge National Laboratory, Tennessee 37831-6036, USA.
Environ Sci Technol. 2001 Jan 15;35(2):365-73. doi: 10.1021/es001445q.
Strontium-90 is a major hazardous contaminant of radioactive wastewater and its processing sludges at many Department of Energy (DOE) facilities. In the past, such contaminated wastewater and sludge have been disposed in soil seepage pits, lagoons, or cribs often under highly perturbed alkaline conditions (pH > 12) where 90Sr solubility is low and its adsorption to surrounding soil is high. As natural weathering returns these soils to near-neutral or slightly acidic conditions, the adsorbed and precipitated calcium and magnesium phases, in which 90Sr is carried, change significantly in both nature and amounts. No comprehensive computational method has been formulated previously to quantitatively simulate the dynamics of 90Sr in the soil-groundwater environment under such dynamic and wide-ranging conditions. A computational code, the Hydrologic Utility Model for Demonstrating Integrated Nuclear Geochemical Environmental Responses (HUMDINGER), was composed to describe the changing equilibria of 90Sr in soil based on its causative chemical reactions including soil buffering, pH-dependent cation-exchange capacity, cation selectivity, and the precipitation/dissolution of calcium carbonate, calcium hydroxide, and magnesium hydroxide in response to leaching groundwater characteristics including pH, acid-neutralizing capacity, dissolved cations, and inorganic carbonate species. The code includes a simulation of one-dimensional transport of 90Sr through a soil column as a series of soil mixing cells where the equilibrium soluble output from one cell is applied to the next cell. Unamended soil leaching and highly alkaline soil treatments, including potassium hydroxide, sodium silicate, and sodium aluminate, were simulated and compared with experimental findings using large (10 kg) soil columns that were leached with 90Sr-contaminated groundwater after treatment. HUMDINGER's simulations were in good agreement with dynamic experimental observations of soil exchange capacity, exchangeable cations, total 90Sr, and pH values of layers within the soil columns and of column effluents.
锶-90是美国能源部(DOE)许多设施中放射性废水及其处理污泥的主要有害污染物。过去,这类受污染的废水和污泥通常在高度扰动的碱性条件(pH>12)下被处置在土壤渗坑、泻湖或围 cribs中,在这种条件下,90Sr的溶解度较低,且其对周围土壤的吸附性较高。随着自然风化使这些土壤恢复到近中性或微酸性条件,其中携带90Sr的吸附和沉淀的钙和镁相在性质和数量上都会发生显著变化。此前尚未制定出全面的计算方法来定量模拟在这种动态和广泛条件下90Sr在土壤-地下水环境中的动态变化。编写了一个计算代码,即用于演示综合核地球化学环境响应的水文实用模型(HUMDINGER),以根据其相关化学反应描述土壤中90Sr的变化平衡,这些反应包括土壤缓冲、pH值依赖性阳离子交换容量、阳离子选择性以及碳酸钙、氢氧化钙和氢氧化镁的沉淀/溶解,以响应包括pH值、酸中和能力、溶解阳离子和无机碳酸盐物种在内的淋滤地下水特征。该代码包括对90Sr通过土壤柱的一维传输进行模拟,将其作为一系列土壤混合单元,其中一个单元的平衡可溶性输出应用于下一个单元。模拟了未改良土壤淋滤以及包括氢氧化钾、硅酸钠和铝酸钠在内的高碱性土壤处理,并将其与使用大型(10千克)土壤柱进行的实验结果进行比较,这些土壤柱在处理后用受90Sr污染的地下水进行淋滤。HUMDINGER的模拟结果与土壤柱内各层以及柱流出物的土壤交换容量、可交换阳离子、总90Sr和pH值的动态实验观测结果高度一致。