Stanford Synchrotron Radiation Lightsource, SLAC National Accelerator Laboratory , Menlo Park, California 94025, United States.
Department of Environmental Earth System Science, Stanford University , Stanford, California 94305, United States.
Environ Sci Technol. 2017 Oct 3;51(19):10954-10964. doi: 10.1021/acs.est.7b02203. Epub 2017 Sep 21.
Aquifers in the Upper Colorado River Basin (UCRB) exhibit persistent uranium (U) groundwater contamination plumes originating from former ore processing operations. Previous observations at Rifle, Colorado, have shown that fine grained, sulfidic, organic-enriched sediments accumulate U in its reduced form, U(IV), which is less mobile than oxidized U(VI). These reduced sediment bodies can subsequently act as secondary sources, releasing U back to the aquifer. There is a need to understand if U(IV) accumulation in reduced sediments is a common process at contaminated sites basin-wide, to constrain accumulated U(IV) speciation, and to define the biogeochemical factors controlling its reactivity. We have investigated U(IV) accumulation in organic-enriched reduced sediments at three UCRB floodplains. Noncrystalline U(IV) is the dominant form of accumulated U, but crystalline U(IV) comprises up to ca. 30% of total U at some locations. Differing susceptibilities of these species to oxidative remobilization can explain this variability. Particle size, organic carbon content, and pore saturation, control the exposure of U(IV) to oxidants, moderating its oxidative release. Further, our data suggest that U(IV) can be mobilized under deeply reducing conditions, which may contribute to maintenance and seasonal variability of U in groundwater plumes in the UCRB.
科罗拉多河上游流域(UCRB)的含水层存在着持续的铀(U)地下水污染羽流,这些污染羽流源自以前的矿石加工作业。科罗拉多州里夫勒(Rifle)的先前观测结果表明,细粒、含硫、富含有机物的沉积物会以还原态的 U(IV)形式积累 U,其移动性不如氧化态的 U(VI)。这些还原沉积物随后可以作为次要来源,将 U 释放回含水层。有必要了解 U(IV)在整个流域污染场地的还原沉积物中的积累是否是一个普遍过程,以限制积累的 U(IV)形态,以及定义控制其反应性的生物地球化学因素。我们已经在 UCRB 的三个洪泛区调查了富含有机物的还原沉积物中 U(IV)的积累情况。非晶质 U(IV)是积累 U 的主要形式,但在某些地点,晶质 U(IV)占总 U 的比例高达约 30%。这些物质的不同氧化还原敏感性可以解释这种变异性。颗粒大小、有机碳含量和孔隙饱和度控制着 U(IV)与氧化剂的接触程度,从而调节其氧化释放。此外,我们的数据表明,U(IV)可以在深度还原条件下被迁移,这可能导致 UCRB 地下水羽流中 U 的维持和季节性变化。