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Copper isotope fractionation in acid mine drainage

机译:酸性矿山排水中的铜同位素分馏

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摘要

We measured the Cu isotopic composition of primary minerals and stream water affected by acid mine drainage in a min_eralized watershed (Colorado, USA). The δ~65С_u values (based on ~65С_u/(63)С_u) of enargite (δ~(65)C_u = _0.01 ± 0.10%0; 2_a) and chalcopyrite (δ~65C_u = 0.16 ± 0.10%0) are within the range of reported values for terrestrial primary Cu sulfides (-1%0 __ δ~65C_u __ 1%,). These mineral samples show lower δ~65C_u values than stream waters (1.38%0 __ δ~65C_u __ 1.69%0). The average isotopic fractionation (~A_aq-min = δ~65С_u_aq _ δ~65Cu_min, where the latter is measured on mineral samples from the field system), equals 1.43 ± 0.14%0 and 1.60 ± 0.14%0 for chalcopyrite and enargite, respectively. To interpret this field survey, we leached chalcopyrite and enargite in batch experiments and found that, as in the field, the leachate is enriched in ~65C_u relative to chalcopyrite (1.37 ± 0.14%0) and enargite (0.98 ± 0.14%0) when microorganisms are absent. Leaching of minerals in the presence of Acidithiobacillus ferrooxidans results in smaller average fractionation in the opposite direction for chalcopyrite (Δ_aq-min° = _0.57 ± 0.14%0, where min° refers to the starting mineral) and no apparent fractionation for enargite (Δ_aq-min° = 0.14 + 0.14%0). Abiotic fractionation is attributed to preferential oxidation of ~65C_u+ at the interface of the isoto_pically homogeneous mineral and the surface oxidized layer, followed by solubilization. When microorganisms are present, the abiotic fractionation is most likely not seen due to preferential association of ~65Cu_aq with A. ferrooxidans cells and related precipitates. In the biotic experiments, Cu was observed under ТЕМ to occur in precipitates around bacteria and in intracel_lular polyphosphate granules. Thus, the values of δ~65C_u in the field and laboratory systems are presumably determined by the balance of Cu released abiotically and Cu that interacts with cells and related precipitates. Such isotopic signatures resulting from Cu sulfide dissolution should be useful for acid mine drainage remediation and ore prospecting purposes.
机译:我们在矿化流域(科罗拉多州,美国)中测量了受酸性矿山排水影响的主要矿物和溪流水的铜同位素组成。辉镁石(δ〜(65)C_u = _0.01±0.10%0; 2_a)和黄铜矿(δ〜65C_u = 0.16±0.10%0)的δ〜65С_u值(基于〜65С_u/(63)С_u)在地面原生铜硫化物的报告值范围内(-1%0 __δ〜65C_u __ 1%)。这些矿物质样品的δ〜65C_u值比溪流水低(1.38%0 __δ〜65C_u __ 1.69%0)。同位素平均分馏(〜A_aq-min =δ〜65С_u_aq_δ〜65Cu_min,后者是从田间系统的矿物样品中测得的)分别等于黄铜矿和堇青石的1.43±0.14%0和1.60±0.14%0 。为了解释这一现场调查,我们在批量实验中浸出了黄铜矿和镁辉石,发现与田间一样,渗滤液相对于黄铜矿(1.37±0.14%0)和辉镁石(0.98±0.14%0)富含〜65C_u。微生物不存在。在酸性铁氧体氧化亚铁细菌存在下浸出矿物会导致黄铜矿在相反方向上的平均分馏较小(Δ_aq-min°= _0.57±0.14%0,其中min°是指起始矿物),而对辉镁石没有明显的分馏( Δ_aq-min°= 0.14 + 0.14%0)。非生物分离是由于〜65C_u +在同位素均质矿物和表面氧化层的界面上优先氧化,然后溶解。当存在微生物时,由于〜65Cu_aq与A.ferrooxidans细胞及相关沉淀物的优先结合,最有可能看不到非生物分离。在生物实验中,在ТЕМ下观察到Cu出现在细菌周围的沉淀物中以及细胞内的多磷酸盐颗粒中。因此,据推测,在田间和实验室系统中,δ〜65C_u的值取决于非生物释放的铜与与细胞及相关沉淀物相互作用的铜的平衡。由硫化铜溶解产生的这种同位素特征应可用于酸性矿山排水修复和找矿目的。

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