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210 Pb and 210 Po in Geological and Related Anthropogenic Materials: Implications for Their Mineralogical Distribution in Base Metal Ores

机译:地质及相关人为物质中的210 Pb和210 Po:对贱金属矿石中矿物学分布的影响

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The distributions of 210 Pb and 210 Po, short half-life products of 238 U decay, in geological and related anthropogenic materials are reviewed, with emphasis on their geochemical behaviours and likely mineral hosts. Concentrations of natural 210 Pb and 210 Po in igneous and related hydrothermal environments are governed by release from crustal reservoirs. 210 Po may undergo volatilisation, inducing disequilibrium in magmatic systems. In sedimentary environments (marine, lacustrine, deltaic and fluvial), as in soils, concentrations of 210 Pb and 210 Po are commonly derived from a combination of natural and anthropogenic sources. Enhanced concentrations of both radionuclides are reported in media from a variety of industrial operations, including uranium mill tailings, waste from phosphoric acid production, oil and gas exploitation and energy production from coals, as well as in residues from the mining and smelting of uranium-bearing copper ores. Although the mineral hosts of the two radionuclides in most solid media are readily defined as those containing parent 238 U and 226 Ra, their distributions in some hydrothermal U-bearing ores and the products of processing those ores are much less well constrained. Much of the present understanding of these radionuclides is based on indirect data rather than direct observation and potential hosts are likely to be diverse, with deportments depending on the local geochemical environment. Some predictions can nevertheless be made based on the geochemical properties of 210 Pb and 210 Po and those of the intermediate products of 238 U decay, including isotopes of Ra and Rn. Alongside all U-bearing minerals, the potential hosts of 210 Pb and 210 Po may include Pb-bearing chalcogenides such as galena, as well as a range of sulphates, carbonates, and Fe-oxides. 210 Pb and 210 Po are also likely to occur as nanoparticles adsorbed onto the surface of other minerals, such as clays, Fe-(hydr)oxides and possibly also carbonates. In rocks, unsupported 210 Pb- and/or 210 Po-bearing nanoparticles may also be present within micro-fractures in minerals and at the interfaces of mineral grains. Despite forming under very limited and special conditions, the local-scale isotopic disequilibrium they infer is highly relevant for understanding their distributions in mineralized rocks and processing products.
机译:审查了210 Pb和210 Po(238 U衰变的短半衰期产物)在地质和相关人为物质中的分布,重点是它们的地球化学行为和可能的矿物宿主。火成岩及相关热液环境中天然210 Pb和210 Po的浓度受地壳储层释放的控制。 210 Po可能会挥发,从而在岩浆系统中引起不平衡。在沉积环境(海洋,湖泊,三角洲和河流)中,例如在土壤中,210 Pb和210 Po的浓度通常来自自然和人为来源。据报道,各种工业操作产生的介质中两种放射性核素的浓度都有所增加,这些介质包括铀厂尾矿,磷酸生产产生的废物,煤炭开采的石油和天然气以及能源生产,以及铀矿开采和冶炼的残留物中。轴承铜矿。尽管在大多数固体介质中,两种放射性核素的矿物主体很容易定义为包含母体238 U和226 Ra的矿物主体,但它们在某些含热液含铀矿石中的分布以及加工这些矿石的产品受到的约束要少得多。目前对这些放射性核素的大部分理解是基于间接数据而不是直接观察,并且潜在的宿主可能多种多样,其行为取决于当地的地球化学环境。尽管如此,仍可以根据210 Pb和210 Po的地球化学性质以及238 U衰变的中间产物(包括Ra和Rn的同位素)的地球化学性质做出一些预测。除所有含U的矿物外,潜在的210 Pb和210 Po主体可能包括含Pb的硫族化物,如方铅矿,以及各种硫酸盐,碳酸盐和Fe-氧化物。 210 Pb和210 Po也可能作为纳米颗粒吸附到其他矿物(例如粘土,Fe-(氢氧化)氧化物,也可能是碳酸盐)表面上而出现。在岩石中,无支撑的210 Pb和/或210 Po的纳米颗粒也可能存在于矿物的微裂缝中以及矿物颗粒的界面处。尽管形成是在非常有限和特殊的条件下进行的,但他们推断出的局部尺度的同位素不平衡与理解其在矿化岩石和加工产品中的分布高度相关。

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