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1.
金川镍矿浮选尾矿数量巨大,含有相当可观的有价金属,其中有价金属的回收受到越来越多的关注。金川老尾矿库尾矿砂中Ni和Cu赋存状态复杂,水溶性矿物态、可交换离子态、碳酸盐态、结晶度较差的Fe氧化物态、结晶度较好的Fe氧化物态、硫化物态和残渣态中都含有数量不等的有价金属Ni和Cu;尾矿砂风化作用释放的金属阳离子大多数在发生氧化的硫化物位置原位发生水解沉淀形成次生矿物,有价金属Ni和Cu在尾矿库中没有发生明显的富集。金川镍矿尾矿砂中Ni和Cu适于用化学酸溶浸出的方法进行二次回收。 相似文献
2.
《矿物岩石地球化学通报》2015,(5)
金川铜镍硫化矿尾矿砂富含Cu、Ni和Co等金属,为对其进行回收,对新尾矿库不同深度的尾矿砂分别进行了直接硫酸酸溶浸出与A.f.-硫酸酸溶联合浸出实验,利用ICP-AES分析了不同阶段浸出液中Cu2+、Ni2+、Co2+含量。实验结果表明,A.f.-硫酸酸溶联合浸出工艺对尾矿砂中有价金属Cu、Ni和Co的浸出效果优于单独酸溶浸出工艺。其中,A.f.-硫酸酸溶联合浸出法对1m深度的尾矿砂中Cu、Ni、Co的浸出率最高,分别达到95.78%、98.01%和75.13%,而单独硫酸酸溶作用的离子浸出率分别为75.69%、74.33%和42.33%。 相似文献
3.
本文以金川铜镍硫化物精矿为研究对象,对比研究了A.f.菌浸出与硫酸酸溶浸出对铜镍硫化物精矿中有价金属Co、Ni和Cu的提取效果。为了进一步优化硫化物精矿中有价金属Co、Ni和Cu浸出效果,考察了微生物-硫酸浸出与硫酸-微生物浸出对精矿中Co、Ni和Cu提取的影响。结果表明:Co2+、Ni2+、Cu2+微生物-硫酸浸出率可分别达到85.05%、98.32%和95.31%。微生物-硫酸浸出加速了硫化物矿物的溶解,促进了硫化物矿物中有价金属Co、Ni、Cu的浸出,大大提高了有价金属Co2+、Ni2+、Cu2+的浸出率。 相似文献
4.
金川铜镍硫化矿尾矿砂数量巨大,其中Ni、Cu和Co等有价金属种类较多,含量较为丰富,蕴含着巨大的经济价值。本文研究了氧化亚铁硫杆菌对金川铜镍尾矿砂提取有价金属效果的影响,在选取金川新尾矿库中心钻孔尾矿砂样品与氧化亚铁硫杆菌作用不同时间的基础上进行化学酸溶,利用电感耦合等离子体发射光谱仪(ICP-AES)分析了溶液中Cu2+、Ni2+、Co2+含量,并通过离子浸出率来表征微生物对尾矿中有价金属提取的影响效果。结果表明,尾矿砂直接化学酸溶后Cu2+、Ni2+浸出率分别为73.78%和69.87%,Co2+浸出率仅为39.57%;而氧化亚铁硫杆菌先与尾矿砂作用后再进行硫酸酸溶,其Cu2+、Ni2+总浸出率均可达到90%以上,Co2+总浸出率也可达到70%以上。实验结果证明氧化亚铁硫杆菌的参与促进了尾矿砂中Cu2+、Ni2+、Co2+的浸出。 相似文献
5.
东昆仑夏日哈木超大型岩浆镍钴硫化物矿床的工业价值，不仅取决于矿石中Co、Ni的含量，还取决于钴和镍关键金属的赋存状态和分布规律。笔者利用全自动矿物分析系统钻孔样品分析，确定Co和Ni在样品中有2种赋存状态：独立钴、镍矿物和含Co、Ni矿物。对钴、镍金属矿物进行原位主、微量元素分析发现，Co在钴、镍金属矿物中含量由高到低为：辉砷钴矿>砷镍矿、方硫铁镍矿、镍黄铁矿>红砷镍矿、磁铁矿>磁黄铁矿、黄铜矿；Ni在钴、镍金属矿物中含量由高到低为：砷镍矿、红砷镍矿>硫铋镍矿、方硫铁镍矿、镍黄铁矿>辉砷钴矿>磁铁矿、磁黄铁矿、黄铜矿。选择钻孔中体积分数占比最高的磁黄铁矿、镍黄铁矿和黄铜矿，进行原位核–边微量元素及面扫描分析发现，Co、 Ni在镍黄铁矿和黄铜矿单颗粒尺度上是均一分布的，两种矿物的Co/Ni值变化不大，表明矿物没有受到热液作用影响。然而，Ni在磁黄铁矿中分布不均一，并且矿物的Co/Ni值变化较大，表明磁黄铁矿对热液作用更为敏感。矿物原位主、微量元素分析结果显示，镍黄铁矿中的Co、Ni含量与镍、钴独立矿物接近，远超岩体中其他含钴、镍金属硫化物。因此，含Ni... 相似文献
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幔源岩浆形成与演化过程中镍(Ni)、钴(Co)具有相似的地球化学行为。金川岩浆铜镍硫化物矿床以Ni、铜(Cu)为主要矿种,Co为伴生,Ni、Co在金川矿床中的空间分布规律同步变化,然而其Ni/Co比值(36.7)远高于地幔值(18.2)。这表明在金川矿床形成过程中Ni-Co发生了共生分离,但Ni-Co分布特征尚不清楚、其控制因素尚不明确。本文对该矿床中主要矿石矿物的Ni、Co含量及分布进行了系统总结,并与脉石矿物进行对比。结果表明矿石矿物镍黄铁矿是最重要的含Ni、Co矿物相,其Ni、Co含量均远高于磁黄铁矿、黄铜矿及脉石矿物。对于脉石矿物,Ni在橄榄石、磁铁矿、铬铁矿内的含量依次降低,在斜方辉石与单斜辉石中含量最低。Co则在铬铁矿、橄榄石内含量依次降低,在斜方辉石、单斜辉石、磁铁矿中含量最低。在硫化物熔离过程中,Ni在硫化物熔体内相容性更强,更加倾向于进入硫化物熔体,使Ni显著富集于硫化物熔体内,而Co则相对富集于硅酸盐熔体内,由此导致Ni-Co解耦。硫化物冷却结晶过程中,Ni、Co倾向于进入最早结晶的单硫化物固溶体(MSS),并在随后分解作用中集中进入镍黄铁矿内,使镍黄铁矿成为金川矿... 相似文献
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攀西红格钒钛磁铁矿矿田白草矿区发育富钴硫化物矿物,关于其成因和形成环境方面的研究较为薄弱。本文采用矿物学、矿物化学、地球化学等方法对其进行系统研究。矿石中主要富钴硫化物为磁黄铁矿（Po）、黄铁矿（Py）、镍黄铁矿（Pn）、硫钴镍矿（Se）。磁黄铁矿Co、Ni平均质量分数分别为0.21%、0.42%,Co/Ni平均值为1.10;黄铁矿Co、Ni平均质量分数分别为0.18%、0.29%,Co/Ni平均值为0.77;镍黄铁矿Co、Ni平均质量分数分别为2.67%、34.30%,Ni/Fe平均值为1.08、S/Fe平均值为1.91、M/S#平均值为1.13;硫钴镍矿Co、Ni平均质量分数分别为24.30%、22.90%,Co/Ni平均值为1.06。根据Po-Py矿物温度计,白草矿区富钴硫化物结晶温度在267~490℃之间,表明其形成于中高温的条件。通过与地幔包体镍黄铁矿S/Fe、M/S#特征值的对比,结合磁黄铁矿具有陨硫铁（Tr）同质多象晶体的特征,认为白草矿区硫化物具有地幔源的特征,说明成矿物质来源于地幔。白草矿区钴地球化学特征研究表明,在硫化物熔体分离过程中,钴迁移至单硫化物固溶体形成Po-Py固溶体,再由Po-Py固溶体中迁移至Pn、Se,形成了Se、Pn、Po-Py、Ccp（黄铜矿）中Co质量分数依次递减的现象。 相似文献
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金川矿床位于龙首山隆起带东段，是中国最大的岩浆镍钴（铂族元素）矿床。该矿床中最重要的金属硫化物组合是磁黄铁矿、镍黄铁矿和黄铜矿，仅局部含有微量的辉钴矿等独立钴矿物。全岩成矿元素分析显示：矿石中Co与S、Ni之间呈良好的正相关性，与As相关性较差，Co/Ni随硫化物含量的增加而降低。电子探针分析结果表明：镍黄铁矿中Co含量较高，其含量为0.32%～1.93%，平均为0.81%；磁黄铁矿和黄铜矿（方黄铜矿）中Co的含量较低，变化范围分别为0.02%～0.11%和0.01%～0.08%。元素面扫描结果表明：Co含量较高的部位与镍黄铁矿范围完全一致，说明Co主要赋存于镍黄铁矿中。金川矿床整体Co/Ni平均值为0.042，与全球典型橄榄岩相地幔Co/Ni值（0.055）相似，表明其岩浆源区主要为橄榄岩相。高程度的部分熔融可能是导致其母岩浆中Co绝对含量较高，但Co/Ni值相对较低的原因之一。硫化物熔离时，Co更倾向于进入硫化物；但相对于Ni，进入硫化物的Co较少，导致不同矿石类型之间S含量与Co/Ni值之间呈明显的负相关性。硫化物分离结晶作用进一步促使Co向镍黄铁矿中富集。 相似文献
9.
捕虏体麻粒岩是了解下地壳形成和演化的重要样品。汉诺坝新生代玄武岩中的二辉麻粒岩捕虏体样品中富含各种硫化物相,主要类型有:①孤立产出的球状出溶硫化物;②矿物颗粒之间或颗粒内的粗晶硫化物;③次生硫化物包裹体群;④裂隙充填硫化物。电子探针分析表明,硫化物的矿物成分均为贫镍磁黄铁矿,(Ni+Co+Cu)/Fe(原子比)远小于0.2;(Fe+Cu+Co+Ni)/S(原子比)比地幔岩的磁黄铁矿小,多小于0.875,反映了一种S过饱和环境。各种产状的磁黄铁矿中Au、Ag都有一定的含量,其平均值分别为0.19%～0.22%(Au)、0.01%～0.02%(Ag),反映下地壳的麻粒岩化与金矿化的成因联系。磁黄铁矿的Ni、Co、Cu含量与S正相关,说明微量重金属元素与S具有同源的关系,由于地幔去气伴随S而进入下地壳。 相似文献
10.
金川镍矿浮选尾砂的物质组成及开发应用研究 总被引：5，自引：0，他引：5
选矿尾砂是金川公司最大的工业废弃物和污染源 ,其潜在利用价值、治理及其综合利用途径一直是工程技术人员探讨的重大课题。物质组成研究表明 ,金川镍矿选矿尾砂含Ni 0 .2 0 %～ 0 .2 5 %、Cu 0 .16%～0 .2 5 %、Co 0 .0 0 8%～ 0 .0 2 % ,主要矿物为橄榄石、辉石、蛇纹石、透闪石、绿泥石 ,少量为磁黄铁矿、镍黄铁矿、黄铜矿、磁铁矿等 ,大多数颗粒粒径为 5 0～ 14 0 μm。可以通过有价组分的回收、井下充填物料这两种途径综合回收利用 相似文献
11.
Pyrite and pyrrhotite are the principal minerals that generate acid drainage in mine wastes. Low-pH conditions derived from Fe-sulfide oxidation result in the mobilization of contaminant metals (such as Zn, Cd, Ni and Cr) and metalloids (such as As) which are of environmental concern. This paper uses data from detailed mineralogical and geochemical studies conducted at two Canadian tailings impoundments to examine the mineralogical changes that pyrite, pyrrhotite, sphalerite and magnetite undergo during and after sulfide oxidation, and the subsequent release and attenuation of associated trace elements. The stability of sphalerite in tailings impoundments generally is greater than that of pyrrhotite, but less than pyrite. Dissolved Ni and Co derived from Fe sulfides, and to a lesser extent, dissolved Zn and Cd from sphalerite, are commonly attenuated by early-formed Fe oxyhydroxides. As oxidation progresses, a recycling occurs due to continued leaching from low-pH pore waters and because the crystallinity of Fe oxyhydroxides gradually increases which decreases their sorptive capacity. Unlike many other elements, such as Cu, Pb and Cr, which form secondary minerals or remain incorporated into mature Fe oxyhydroxides, Zn and Ni become mobile. Magnetite, which is a potential source of Cr, is relatively stable except under extremely low-pH conditions. A conceptual model for the sequence of events that typically occurs in an oxidizing tailings impoundment is developed outlining the progressive oxidation of a unit of mine waste containing a mixed assemblage of pyrrhotite and pyrite. 相似文献
12.
Björn Öhlander Barbara Müller Mikael Axelsson Lena Alakangas 《Journal of Geochemical Exploration》2007
Metals released from oxidation and weathering of sulphide minerals in mine tailings are to a high degree retained at deeper levels within the tailings themselves. To be able to predict what could happen in the future with these secondarily retained metals, it is important to understand the retention mechanisms. In this study an attempt to use laser ablation high-resolution ICP-MS (LA-ICP-SMS) to quantify enrichment of trace elements on pyrite surfaces in mine tailings was performed. Pyrite grains were collected from a profile through the pyrite-rich tailings at the Kristineberg mine in northern Sweden. At each spot hit by the laser, the surface layer was analyzed in the first shot, and a second shot on the same spot gave the chemical composition of the pyrite immediately below. The crater diameter for a laser shot was known, and by estimating the crater depth and total pyrite surface, the total enrichment on pyrite grains was calculated. Results are presented for As, Cd, Co, Cu, Ni and Zn. The results clearly show that there was an enrichment of As, Cd, Cu and Zn on the pyrite surfaces below the oxidation front in the tailings, but not of Co and Ni. Arsenic was also enriched on the pyrite grains that survived in the oxidized zone. Copper has been enriched on pyrite surfaces in unoxidized tailings in the largest amount, followed by Zn and As. However, only 1.4 to 3.1% of the Cd and Zn released by sulphide oxidation in the oxidized zone have been enriched on the pyrite surfaces in the unoxidized tailings, but for As and Cu corresponding figures are about 64 and 43%, respectively. There were many uncertainties in these calculations, and the results shall not be taken too literally but allowed the conclusion that enrichment on pyrite surfaces is an important process for retention of As and Cu below the oxidation front in pyrite rich tailings. Laser ablation is not a surface analysis technique, but more of a thin layer method, and gives no information on the type of processes resulting in enrichment on the pyrite surfaces. Although only pyrite grains that appeared to be fresh and without surface coatings were used in this study, the possibility that a thin layer of Fe-hydroxides occurred must be considered. Both adsorption to the pyrite directly or to Fe-oxyhydroxides may explain the enrichment of As, Cd, Cu and Zn on the pyrite surfaces, and, in the case of Cu, also the replacement of Fe(II) by Cu(II) in pyrite. 相似文献
13.
《矿物学报》2013,(Z1)
China has accumulated massive fine grained copper mine tailings stocks because of the past mining activities in this area. The tailings contain a variety of heavy metals, and the mass percent of Cu, which is one of the main contaminants in tailings, is up to 0.2601% (analysis by XRF). The Cu can pollute soil and groundwater by rain leaching in the form of Cu(Ⅱ), furthermore ,the fine grained copper-ore-tailings can contaminant larger area by wind for its small granularity ( < 74 μm). The main cause of weathering of mine tailings is due to oxidative dissolution of sulfides. Microorganisms, such as Acidithiobacillus ferrooxidans, play an important role in weathering. These bacteria attach to exposed to mineral surfaces by excreting extracellular polymers and oxidize the sulfide mineral. Some of these bacteria also oxidize Fe2+ to Fe3+ which can chemically oxidize sulfide minerals. These reactions produce voluminous quantities of acid mine drainage and heavy metals which are harmful to the environment and human healthy. This study aims at finding the weathering effects of A. ferrooxidans to Cu(II) pollution of fine grained copper mine tailings, and our experiment applied indigenous A. ferrooxidans FJ-01 to leach the tailings. The optimum test parameters were obtained using shaking flask experiment and SEM observation under the following experimental conditions: 39 days residence time, pulp density 1%-15% (1%, 5% and 15%), 30℃, 120 rpm, pH between 1-3 and redox potential between 400-650 mV. The test results show that the leaching rate of Cu reached 43.1% when the pulp density was 1% after 33 days and kept invariant till the end of the test. In addition, the leaching rate of Cu will decrease as the increase of pulp density, and the maximum rate of 15% pulp density was only 12.5%. From the SEM, it can be seen that the fine grain of tailings flocculated to conglobation under the action of bacterial leaching. 相似文献
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15.
Redistribution of potentially harmful metals and As was studied based on selective extractions in two active sulphide mine tailings impoundments in Finland. The Hitura tailings area contains residue from Ni ore processing, while the Luikonlahti site includes tailings from the processing of Cu–Co–Zn–Ni and talc ores. To characterize the element solid-phase speciation with respect to sulphide oxidation intensity and the water saturation level of the tailings, drill cores were collected from border zones and mid-impoundment locations. The mobility and solid-phase fractionation of Ni, Cu, Co, Zn, Cr, Fe, Ca, Al, As, and S were analysed using a 5-step non-sequential (parallel) selective extraction procedure. The results indicated that metal redistribution and sulphide oxidation intensity were largely controlled by the disposal history and strategy of the tailings (sorting, exposure of sulphides due to delayed burial), impoundment structure and water table, and reactivity of the tailings. Metal redistribution suggested sulphide weathering in the tailings surface, but also in unsaturated proximal areas beside the earthen dams, and in water-saturated bottom layers, where O2-rich infiltration is possible. Sulphide oxidation released trace metals from sulphide minerals at both locations. In the Hitura tailings, with sufficient buffering capacity, pH remained neutral and the mobilized metals were retained by secondary Fe precipitates deeper in the oxidized zone. In contrast, sulphide oxidation-induced acidity and rise in the water table after oxidation apparently remobilized the previously retained metals in Luikonlahti. In general, continuous disposal of tailings decreased the sulphide oxidation intensity in active tailings, unless there was a delay in burial and the reactive tailings were unsaturated after deposition. 相似文献
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Tailings generated during processing of sulfide ores represent a substantial risk to water resources. The oxidation of sulfide minerals within tailings deposits can generate low-quality water containing elevated concentrations of SO4, Fe, and associated metal(loid)s. Acid generated during the oxidation of pyrite [FeS2], pyrrhotite [Fe(1−x)S] and other sulfide minerals is neutralized to varying degrees by the dissolution of carbonate, (oxy)hydroxide, and silicate minerals. The extent of acid neutralization and, therefore, pore-water pH is a principal control on the mobility of sulfide-oxidation products within tailings deposits. Metals including Fe(III), Cu, Zn, and Ni often occur at high concentrations and exhibit greater mobility at low pH characteristic of acid mine drainage (AMD). In contrast, (hydr)oxyanion-forming elements including As, Sb, Se, and Mo commonly exhibit greater mobility at circumneutral pH associated with neutral mine drainage (NMD). These differences in mobility largely result from the pH-dependence of mineral precipitation–dissolution and sorption–desorption reactions. Cemented layers of secondary (oxy)hydroxide and (hydroxy)sulfate minerals, referred to as hardpans, may promote attenuation of sulfide-mineral oxidation products within and below the oxidation zone. Hardpans may also limit oxygen ingress and pore-water migration within sulfide tailings deposits. Reduction–oxidation (redox) processes are another important control on metal(loid) mobility within sulfide tailings deposits. Reductive dissolution or transformation of secondary (oxy)hydroxide phases can enhance Fe, Mn, and As mobility within sulfide tailings. Production of H2S via microbial sulfate reduction may promote attenuation of sulfide-oxidation products, including Fe, Zn, Ni, and Tl, via metal-sulfide precipitation. Understanding the dynamics of these interrelated geochemical and mineralogical processes is critical for anticipating and managing water quality associated with sulfide mine tailings. 相似文献
18.
Coal mine rejects and sulfide bearing coals are prone to acid mine drainage (AMD) formation due to aqueous weathering. These acidic effluents contain dissolved trace and potentially harmful elements (PHEs) that have considerable impact on the environment. The behavior of these elements in AMD is mainly controlled by pH. The focus of the present study is to investigate aqueous leaching of mine rejects for prediction of acid producing potential, rates of weathering, and release of PHEs in mine drainage. Mine reject (MR) and coal samples from the active mine sites of Meghalaya, India typically have high S contents (1.8–5.7% in MR and 1.7–4.7% in coals) with 75–90% of the S in organic form and enrichment of most of the PHEs in rejects. Aqueous kinetic leaching experiments on mine rejects showed high acid producing potential and release of trace and potentially harmful elements. The elements (Sb, As, Cd, Cr, Co, Cu, Pb, Mn, Ni, V and Zn) in mine sample leachates are compared with those in mine waters. The concentrations of Al, Si, P, K, Ti, Mn, Fe, Co, Ni, Cu, Zn and Pb are found to increase with leaching time and are negatively correlated with pH of the solution. The processes controlling the release of these elements are acid leaching, precipitation and adsorption. The critical loads of PHEs in water affected by AMD are calculated by comparing their concentrations with those of regulatory levels. The Enrichment Factors (EFs) and soil pollution indices (SPIs) for the elements have shown that PHEs from coal and mine reject samples are mobilized into the nearby environment and are enriched in the associated soil and sediment. 相似文献