首页> 外文期刊>Journal of Radioanalytical and Nuclear Chemistry: An International Journal Dealing with All Aspects and Applications of Nuclear Chemistry >Sorption and desorption of I-125-, Cs-137(+), Sr-85(2+) and Eu-152,154(3+) on disturbed soils under dynamic flow and static batch conditions
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Sorption and desorption of I-125-, Cs-137(+), Sr-85(2+) and Eu-152,154(3+) on disturbed soils under dynamic flow and static batch conditions

机译:I-125-,Cs-137(+),Sr-85(2+)和Eu-152,154(3+)在扰动土壤上的动态流动和静态批处理条件下的吸附和解吸

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Sorption of radionuclides on homogenized soils (under 2.5 mm grain size) from synthetic groundwater of 8 center dot 10(-3)M ionic strength and pH 8.5 has been studied under dynamic (flow) and static (batch) conditions. The corresponding water-soluble compounds, as carriers in the 10(-6) mol/dm(3) concentration, were added into the SGW prior to the experiments. Soil samples were taken from several locations around the environment of the High Level Waste Storage Facility at Nuclear Research Institute angstrom similar to e angstrom 3/4 plc in 5-100 cm depth. The dynamic experiments were carried out in columns made of PP+PE injection syringes of 17.8 cm length and 2.1 cm in diameter. A multi-head peristaltic pump was used for pumping the water upward through the columns at a seepage velocity of about 0.06 cm/min in average. The radioactive nuclides were added into the water stream individually in a form of a short pulse in 0.1 cm(3) of demineralized water. Dynamic desorption experiments were performed with the same experimental arrangement using a mixture of 10(-2)N H2SO4 and 10(-2)N HNO3 in a volume ratio of 2: 1. Retardation, distribution and hydrodynamic dispersion coefficients during transport of radionuclides were determined by the evaluation of the integral form of a simple advection-dispersion equation, used for fitting experimental data and modeling the theoretical sorption breakthrough and desorption displacement curves. The static experiments were realized in 100 cm(3) plastic bottles stirring 5 g of soil samples with SGW occasionally in a soil to SGW ratio of 1: 10 (m/V). Kinetic parameters including equilibrium sorption activity, activity transfer rate constants and sorption half-times were also determined. The results of dynamic experiments were compared with static sorption experiments.
机译:研究了在动态(流动)和静态(间歇)条件下,从8个中心点10(-3)M离子强度和pH值为8.5的合成地下水对均质土壤(2.5毫米粒度以下)中放射性核素的吸附。在实验之前,将相应的水溶性化合物(浓度为10(-6)mol / dm(3)的载体)添加到SGW中。土壤样品是从核研究所的高级废物存储设施周围环境的几个位置采集的,类似于5-100厘米深度的埃埃3/4 plc。动态实验在长度为17.8 cm,直径为2.1 cm的PP + PE注射器制成的色谱柱中进行。使用多头蠕动泵以平均约0.06 cm / min的渗漏速度将水向上泵送通过色谱柱。将放射性核素以短脉冲的形式分别添加到水流中的0.1 cm(3)的软化水中。使用10(-2)N H2SO4和10(-2)N HNO3的体积比为2:1的混合物,以相同的实验安排进行动态解吸实验。在放射性核素运输过程中,延迟,分布和流体动力扩散系数为通过评估简单对流扩散方程的积分形式确定,用于拟合实验数据并为理论吸附突破和解吸位移曲线建模。静态实验是在100 cm(3)塑料瓶中实现的,该塑料瓶偶尔以5:1的土壤与SGW的比率搅拌5 g带有SGW的土壤样品。还确定了动力学参数,包括平衡吸附活性,活性转移速率常数和吸附半衰期。将动态实验的结果与静态吸附实验进行了比较。

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