Sulfidation and Reoxidation of U(VI)-Incorporated Goethite: Implications for U Retention during Sub-Surface Redox Cycling.

Sulfidation and Reoxidation of U(VI)-Incorporated Goethite: Implications for U Retention during Sub-Surface Redox Cycling.
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DOI:
10.1021/acs.est.2c05314
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发表时间:
2022-12-20
影响因子:
11.4
通讯作者:
Shaw, Samuel
Shaw, Samuel
中科院分区:
环境科学与生态学1区
文献类型:
--
作者:
Stagg, Olwen;Morris, Katherine;Townsend, Luke Thomas;Kvashnina, Kristina O.;Baker, Michael L.;Dempsey, Ryan L.;Abrahamsen-Mills, Liam;Shaw, Samuel

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60多年的核活动造成了全球土地污染和放射性废物的遗留问题。铀(U)是这一遗产的重要组成部分,存在于放射性废物和许多受污染的场地中。含铀铁(氧氢)氧化物可能对环境中的铀迁移提供长期的屏障。然而,由于硫酸盐的微生物还原,铁(羟基)氧化物的还原溶解可在与含水硫化物(硫化)反应时发生,含水硫化物是一种常见的环境物种。在这项工作中,U(VI)-针铁矿最初与硫化物水溶液反应,然后再氧化反应,以进一步了解波动的环境条件下的U物种的长期命运。在硫化的第一天,观察到水U的瞬时释放,可能是由于中间体铀酰(VI)-过硫化物物种。尽管如此,总的U被保留在固相中,在硫化体系中形成纳米晶U(IV)O2,沿着持久的U(V)组分。在再氧化,U与铁(oxyhydr)氧化物相作为吸附的铀酰(约65%)或纳入U(35%)的物种。这些研究结果支持铁(oxyhydr)氧化物作为一个障碍,在环境中的U迁移的总体概念,即使在波动的氧化还原条件下。U(VI)−针铁矿与硫化物水溶液的反应会导致微量铀水溶液的短暂再活化,并使U(IV)O2长期固相保留。
Over 60 years of nuclear activity have resulted in a global legacy of contaminated land and radioactive waste. Uranium (U) is a significant component of this legacy and is present in radioactive wastes and at many contaminated sites. U-incorporated iron (oxyhydr)oxides may provide a long-term barrier to U migration in the environment. However, reductive dissolution of iron (oxyhydr)oxides can occur on reaction with aqueous sulfide (sulfidation), a common environmental species, due to the microbial reduction of sulfate. In this work, U(VI)–goethite was initially reacted with aqueous sulfide, followed by a reoxidation reaction, to further understand the long-term fate of U species under fluctuating environmental conditions. Over the first day of sulfidation, a transient release of aqueous U was observed, likely due to intermediate uranyl(VI)–persulfide species. Despite this, overall U was retained in the solid phase, with the formation of nanocrystalline U(IV)O2 in the sulfidized system along with a persistent U(V) component. On reoxidation, U was associated with an iron (oxyhydr)oxide phase either as an adsorbed uranyl (approximately 65%) or an incorporated U (35%) species. These findings support the overarching concept of iron (oxyhydr)oxides acting as a barrier to U migration in the environment, even under fluctuating redox conditions. Reaction of U(VI)−goethite with aqueous sulfide results in transient remobilization of trace levels of aqueous uranium with long-term solid phase retention of U(IV)O2.
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