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Radium isotope response to aquifer storage and recovery in a sandstone aquifer

机译:镭同位素对砂岩含水层的含水层储存和恢复响应

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摘要

Radium isotopes and water-rock interaction were evaluated in an aquifer storage and recovery (ASR) pilot study conducted in 2010-2011 in Minnesota (USA) in order to identify mechanisms governing Ra activities when low-Ra water is recharged into a sandstone aquifer. Groundwater in the aquifer selected for the study, the Cambrian Mt. Simon Sandstone, contains naturally occurring radium that in many areas exceeds United States drinking water standards (185 mBq/L or 5 pCi/L combined Ra-226+Ra-228), highlighting the need to identify the rates and mechanisms by which stored water acquires Ra isotopes. Major element concentrations of recovered water largely resembled recharged water, while Ra activities exceeded the Ra activities of the recharged water. Ra-224 reached similar to 100 mBq/L during the first 8 h of recovery (overall range 15.5-133 mBq/L). Ra-226 and Ra-228 also increased during the 47-day recovery period (23.7-82.5 mBq/L and 33.7-85.5 mBq/L, respectively). Ra isotope ratios indicate the relative contribution of alpha recoil vs. chemical processes (e.g. adsorption/desorption). During recovery, the Ra-224/Ra-228 and Ra-228/Ra-226 ratios declined, approaching their expected limiting values near unity. Collectively, the rates of Ra activity change with time, trends in Ra isotope ratios, barium concentrations, and manganese concentrations suggest that Ra was governed by chemical processes and alpha recoil, in which the half-lives of each Ra isotope determined the primary mechanism(s) controlling radionuclide mobilization from the aquifer solids. Radium-mobilizing processes during storage may include: (1) recharge of low-Ra water into an aquifer containing high-Ra groundwater induced adsorption/desorption disequilibrium and caused net Ra desorption; (2) chemical conditions during storage (e.g. the Ba content of the recharge water or the reducing conditions in the aquifer) could have further released Ra from the aquifer solids or reduced the effectiveness of Ra adso
机译:在Minnesota(USA)在2010-2011的含水层储存和恢复(ASR)试验研究中评估了镭同位素和水岩相互作用,以识别低RA水充电到砂岩含水层时控制RA活动的机制。选择用于研究的含水层的地下水,寒武纪山Simon Sandstone含有天然存在的镭,在许多地区超过美国饮用水标准(185 MBQ / L或5 PCI / L组合RA-226 + RA-228),强调需要识别储存水获取RA同位素的速率和机制。回收水的主要元素浓度大致类似充电水,而RA活性超过了充电水的RA活性。 RA-224在恢复的前8小时内达到类似于100 MBQ / L(总范围15.5-133 MBQ / L)。 RA-226和RA-228在47天的恢复期间也增加(分别为23.7-82.5 MBQ / L和33.7-85.5 MBQ / L)。 Ra同位素比表明α反冲与化学过程的相对贡献(例如吸附/解吸)。在恢复期间,RA-224 / RA-228和RA-228 / RA-226比率下降,接近其预期限制值附近的统一。统称,RA活性变化的时间随时间,RA同位素比,钡浓度和锰浓度的趋势表明,RA由化学方法和α反冲定控,其中每个RA同位素的半衰期确定了主要机制( S)控制从含水层固体的放射性核素培养。储存过程中的镭动过程可包括:(1)将低RA水的再充电含有高RA地下水诱导的吸附/解吸不平衡的含水层,并导致净RA解吸; (2)储存期间的化学条件(例如,充电水的BA含量或含水层中的还原条件)可以进一步从含水层固体中释放RA或降低RA ADSO的有效性

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