Departament de Química Analítica, Universitat de Barcelona, Martí i Franquès 1-11, E-08028 Barcelona, Spain.
Sci Total Environ. 2010 Nov 1;408(23):5966-71. doi: 10.1016/j.scitotenv.2010.05.035. Epub 2010 Sep 17.
A planar-source method, initially designed to obtain diffusion coefficients in compacted clay, is adapted here to determine the apparent diffusion coefficient (D(a)) of radiostrontium in soils representative of the Spanish territory. Experiments were carried out by varying the moisture content (F(moist)), and bulk dry density (ρ(bulk)) of the soil samples, in order to study the influence of these soil packing parameters on D(a) values. The moisture in the soil samples was established as the percentage of occupancy of each soil's field capacity (OFC). For a similar OFC, D(a) values in the examined soils ranged by approximately one order of magnitude (e.g. from 6.2 × 10(-)(11) to 6.5 × 10(-)(12)m(2)s(-)(1), at 100% of OFC; from 3.0 × 10(-)(11) to 3.8 × 10(-)(12)m(2)s(-)(1), at 60% of OFC). For a given soil, D(a) values increased when water content was increased. F(moist), and tortuosity (τ) explained D(a) variability, with R(2) values usually over 0.9. However, no good simple or multiple regressions between the soil packing parameters and D(a) were obtained with the whole dataset of all soils, which indicated that soil sorption capacity affects the diffusion of reactive radionuclides in soils. The inclusion of calculated K(d) values in the multiple regressions improved the correlations in all cases. Finally, D(a) values were compared with those obtained by the application of a half-cell method. The values of D(a) obtained by the planar-source methods were systematically lower than the half-cell ones, with a good correlation between the D(a) derived from both methods (R(2)=0.98).
平面源法最初设计用于获得压实粘土中的扩散系数,这里将其改编用于确定代表西班牙领土的土壤中放射性锶的表观扩散系数(D(a))。通过改变土壤样品的含水率(F(moist))和体干密度(ρ(bulk))来进行实验,以研究这些土壤包装参数对 D(a)值的影响。土壤样品中的水分是根据每个土壤田间持水量(OFC)的占用百分比来确定的。对于类似的 OFC,在所研究的土壤中,D(a)值的范围约为一个数量级(例如,在 100%的 OFC 时,从 6.2×10(-)(11)到 6.5×10(-)(12)m(2)s(-)(1);在 60%的 OFC 时,从 3.0×10(-)(11)到 3.8×10(-)(12)m(2)s(-)(1))。对于给定的土壤,当含水量增加时,D(a)值增加。F(moist)和曲折度(τ)解释了 D(a)的可变性,R(2)值通常超过 0.9。然而,对于所有土壤的数据集,没有得到土壤包装参数与 D(a)之间的良好简单或多元回归,这表明土壤吸附能力会影响反应性放射性核素在土壤中的扩散。在多元回归中包含计算出的 K(d)值可提高所有情况下的相关性。最后,将 D(a)值与应用半电池方法获得的值进行了比较。平面源方法获得的 D(a)值系统地低于半电池方法的值,两种方法得到的 D(a)值之间具有良好的相关性(R(2)=0.98)。