首页> 外文期刊>Geochemistry: exploration, environment, analysis >Geochemical effects of deeply buried Cu—Au mineralization ontransported regolith in an arid terrain
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Geochemical effects of deeply buried Cu—Au mineralization ontransported regolith in an arid terrain

机译:干旱地区深埋Cu-Au矿化对运移重生岩的地球化学影响

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The presence of transported regolith commonly restricts the disper-sion of trace elements from mineralized bedrock or in situ regolith to surface,especially in arid terrains. Where dispersion through transported regolith does occur,low-concentration haloes derived from mineralization may be masked by othersurficial geochemical processes. Substantial changes to the mineralogy and mineraldistribution within transported regolith, as a result of 1-1+ released from oxidizingsulphide mineralization and other reactions, has been recognized in a number ofregolith settings. Various approaches to detection of such features have beendeveloped, but their application has met with limited success in arid environmentstypical of Australia. The Mandamah Cu—Au deposit, in central—western New SouthWales, is covered by c. 50 m of transported regolith and c. 30 m of saprolite. The top2 m of regolith in the region is characterized by an organic-rich surface layer withneutral pH, followed by a high-pH zone with pedogenic carbonate development anda lower selvage of gypsum, and an underlying low-pH zone displaying Fe mottling.The principal effects of mineralization in the upper transported regolith aredepletion of ammonium acetate-extractable Ca, S and Na, a reduction in the cationexchange capacity, the presence of non-carbonate alkalinity and a low soil electricalconductivity. There is no indication of transport to surface and accumulation ofelements related to the mineralization, such as Cu, Mo, Au or S. A model to accountfor these patterns, based partly on existing dispersion models, involves a progradestage of alteration of clay mineralogy with redistribution of carbonates and someelements as a result of the development of an acid chimney above the oxidizingmineralization during periods of elevated water tables and a subsequent retrogradestage involving a redistribution of mobile elements into the area of the former acidchimney following the onset of more arid conditions.
机译:运移的碎屑岩的存在通常限制了微量元素从矿化基岩或原位碎屑岩向地表的扩散,特别是在干旱地区。在确实发生了通过运输的碎屑岩的分散的情况下,源自矿化的低浓度晕圈可能会被其他表面地球化学过程掩盖。在许多稀土矿环境中,已认识到由于氧化硫化物矿化和其他反应释放出的1-1 +,导致运输的稀土矿中矿物学和矿物分布发生了实质性变化。已经开发了各种检测这种特征的方法,但是它们的应用在澳大利亚典型的干旱环境中取得了有限的成功。位于新南威尔士州中西部的Mandamah Cu-Au矿床由c覆盖。 50 m运输的碎石和c。 30 m腐泥土。该区域顶部的2 m砾岩的特征是富含有机物的表面层具有pH值呈中性,其后是高pH值带,形成成碳酸盐碳酸盐和较低的石膏边缘,以及下面的低pH值带,表现出铁斑点。上部运输的碎屑岩中矿化的影响是:乙酸铵可提取的Ca,S和Na的耗竭,阳离子交换能力的降低,非碳酸盐碱度的存在以及土壤电导率的降低。没有迹象表明与矿化有关的元素迁移到地面和元素的积累,例如Cu,Mo,Au或S。一种解释这些模式的模型(部分基于现有的分散模型)涉及粘土矿物学改变的再发展阶段,并重新分布。碳酸盐和某些元素的形成是由于在地下水位升高期间在氧化矿化作用上方形成了一个酸性烟囱,以及随后的逆行阶段,其中涉及在更干旱的条件下将活动元素重新分配到前酸性烟囱的区域中。

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