江苏六合新生代玄武岩中地幔捕虏体的硫化物相研究

江苏六合一带碱性玄武岩中的出露有以尖晶石二辉橄榄岩为主的地幔捕虏体,这些地幔矿物中普遍有硫化物相出现：（１）被寄主矿物捕获的早期硫化物颗粒。（２）产于矿物晶粒边界或次生裂隙充填物,（３）硫化物包裹体,包括单相硫的包裹体、硫化物－玻璃两相熔体包裹体和ＣＯ／２－硫化物－玻璃（含硅酸盐子矿物）的多相包裹体,电子探针分析表明,硫化物包裹体比例隙中硫化物具有更高的相对Ｆｅ和Ｓ含量,较低的Ｎｉ含量。硫化物包裹     

硫化物固—液界面电化学效应实验探讨

硫化物作为一类重要的常见矿物，目前国内外对其表面矿物学特征研究有限。具体到硫化物固－液界面处的行为机理，前人的研究程度就更低了。笔者自行设计了一个Fe1-xS-Cr^6 原电池，通过实测电动势（E），t-E关系曲线，溶液可见光吸收谱及其λ－A关系曲线，阐明硫化物与Cr^6＋溶液间的界面行为机理。认为其界面行为过程为；硫化物溶解→离子反应（氧化还原）→吸附Cr^3 。该原电池与一般原电池结构不同，其主要差别在于将反应电极和测量电极分开，从而解决电极反应过程中的浓度极化问题，提高了电化学实验的精度。该研究成果有助于揭示矿物－液体相互作用机理，完善和丰富表面矿物学研究内容，深化化界面成矿理论，并对环境治理，矿物材料应用等开发领域具有重要的参考价值。     

桃园金矿和床物质成分的初步研究

桃园金矿成因比较复杂，岩矿测试和电镜扫描研究表明，金矿矿物组合可划分为金－石英－细粒黄铁矿－毒矿型，金－石英－银－多金属硫化物型；金－石英－自形黄铁矿３种类型，通过对矿石的矿物组分和化学成分，以及金，银的赋存状态研究，认为桃园金矿的矿石属于金矿矿物极细，而矿物组成比较复杂的矿石类型。     

硫化物硫床氧化带砷酸盐矿物的地质找矿意义

砷酸盐矿物是主要产出于硫化物矿床氧化带中的次生矿物,在自然界中已发现２５０多种,我国目前仅发现该类矿物３８种。砷酸盐矿物的生成与原生矿石的矿物成分及其数量、气候条件和介质条件等因素密切相关。毒砂及含砷矿物和黄铜矿、黄铁矿、磁黄铁矿、方铅 １、闪锌矿等硫化物的大理存在是形成砷酸盐酸物的物质基础。该类矿物一般多形成于温湿多雨的热带－亚热带气候区域和放围岩为碳酸盐岩的生－中性的介质环境中。     

内生金矿床的成因：基本模式

金矿床以具有仅限于某一类金矿床的典型矿物组合（金－黄铁矿－毒砂；金－多金属－硫化物；金－碲化物；金－辉锑矿；金－辰砂）之一为特征。特征的矿物组合主要受沉淀环境的ＰＨ值和温度变化的控制。具有前３种矿物组合的金矿物的金矿床起源于花岗岩类或岩浆体系有关的流体，具有后２种矿物组合的金矿床起源于壳下非岩浆流体。     

秦岭卡林型金矿床金、砷地球化学探讨

讨论了秦岭卡林型金矿床中Ａｕ 、Ａｓ 的元素地球化学、矿物学特征。在含矿岩系中获得的Ａｕ、Ａｓ 等成矿元素初始含量较高,且主要集中在成岩黄铁矿中。在矿石样品中对含砷硫化物矿物的研究表明,Ａｕ 、Ａｓ 在矿物显微结构中具有强的正相关性。在大量金进入到硫化物结构之前,就已有［ＡｓＳ］３ － 的存在。在含砷硫化物矿物中,金多半以一种带电类型（Ａｕ３ ＋） 存在, 它很可能替代铁位置上的过剩砷, 以固溶体方式沉淀于硫化物矿物中。此时, 黄铁矿构成（Ａｕ３ ＋ ,Ｆｅ２ ＋）（［ＡｓＳ］３ － ［Ｓ２］２ － ）,毒砂构成（Ａｕ３ ＋ ,Ｆｅ２ ＋）（［ＡｓＳ］３ － ［ＡｓＳ］３ －） 。通过电子探针（ＥＭＰ） 和透射电镜（ＴＥＭ） 对秦岭卡林型金矿含砷硫化物矿物中金的赋存状态的研究表明,在金的成矿作用早期阶段, 金主要以固溶体形式优先富集于含砷黄铁矿和毒砂及砷黝铜矿之中,并且认为是以金的氧化和砷的还原的共沉淀方式发生的。在此之后的金成矿作用晚期阶段,由于热液蚀变和结晶作用程度的增高,寄主矿物耐熔性质相对降低,加之金本身的聚集能力,和因过量砷加入而造成的含砷硫化物矿物的晶格缺陷,致使已形成的固溶体金以“出溶”形式发生再分布,赋存于硫化物矿物晶粒     

广西德保铜锡矿床氧化带产出的砷酸盐矿物

广西德保矿区是我国最重要的砷酸盐矿物产区，已发现有17种砷酸盐矿物，其中钡毒铁石，砷铜矾等12种为在国内首次发现，文中提供了其中一些重要新发现矿物较详细的矿物学数据，初步阐述了该类矿物在德保铜锡矿床氧化带的共生组合特性，指出该类矿物是矽卡岩型铜－锡矿床以及铜铅锌等多金属硫化物矿床的重要找矿标志。     

热液脉型铅-锌-银矿床富铁闪锌矿中硫化物包裹体成因探讨

通过对热液脉型的铅－锌－银矿床（３个）和银矿床（１个）和闪锌矿中硫化物包囊体的特征研究表明,石英－硫化物阶段富铁闪锌矿（主矿物）的硫化物包裹体十分发育：沿生长带产出的乳滴状黄铜矿与主矿物为共同沉淀成因;沿穿切主矿物的黄铜矿或石英细脉两侧,和受粗粒黄铜矿溶蚀的富铁闪锌矿近接触部位发育的乳滴状黄铜矿为渗透－交代产物;沿解理（裂隙）或粒间、粒内产出的各种形态磁黄铁矿是充填－交代的结果;沿解理分布的脉状毒     

陕西小秦岭金矿床中金的赋存状态及分布规律

陕西小秦岭脉状金矿床中，金的赋存状态及其分布与硫化物的发育程度密切相关，金优先赋存于硫化矿物中，只有当硫化物不发育时，才主要以金矿物形式赋存于石英等矿物中。金矿物的Ａｇ／Ａｕ比率主要受成矿温度、硫化物发育程度、成矿热液中Ｃｌ／Ｓ浓度比值等因素制约。     

内蒙古大井矿床中银矿物的研究

本文总结了内蒙古大井矿床中银矿物的类型，产出特征以及矿物命名的问题，详细描述了黝铜矿族，浓红银矿，脆银矿，自然银以及含银的铅－铋（锑）硫盐类矿物等主要银矿物的产出状态和化学成分特征，并讨论了相应的形成条件，同时指出本区银矿物主要形成于两个矿化阶段，即：早期黄铜矿－黄铁矿阶段，主要形成了黝铜矿族的含银矿物以及辉锑银矿，硫锑铜银矿等含铜的硫盐类矿物，晚期方铅矿－闪锌矿阶段，形成的银矿物种类较为繁杂，除形成黝铜矿族矿物外，多数含铅，铋的硫盐矿物以及自然银、硫化物和浓红银矿、脆银矿等无铜的简单硫盐等均是在这一阶段形成。     

硫化物矿物氧化反应动力学实验研究

硫化物矿床和含硫化物矿床（如中高硫煤）在开发过程中由于氧化作用向环境释放大量的酸、硫酸盐、重金属及其它有害物质,造成一定范围内的次生地球化学异常和环境污染;而中国大陆硫化物的排放量2010年将达到39．1×10 6 t。因此,人们对硫化物矿物在表生环境下的氧化行为日益重视。硫化物矿物的氧化速率受矿物本身物理化学特性（组成、结构、表面性质）和介质条件（溶解氧DO、Fe 3＋浓度、pH、Eh、温度及微生物）等多种因素的控制。在全面分析近年来国内外文献的基础上,系统介绍了硫化物矿物氧化动力学实验研究方法、实验参数的选择、反应机理、反应产物及反应速率等的研究现状。指出今后应加强对初始阶段的氧化反应速率、反应中间产物、多因素的综合作用、分子水平上的反应机理解释等方面的研究。     

嗜酸性氧化亚铁硫杆菌与硫化物矿石相互作用的实验研究

实验研究了嗜酸性氧化亚铁硫杆菌(Acidithiobacillus ferrooxidans,简称A.f)与硫化物矿石之间的相互作用,以观察不同矿石矿物发生微生物氧化和形成次生矿物的差异。采用ICP-OES分析了反应前后溶液成分变化,利用扫描电子显微镜(SEM)、能谱分析(EDS)和X射线衍射(XRD)等分析手段研究了矿石表面形貌的变化和沉淀物的矿物组成。分析结果表明,A.f对同一矿石中不同矿物作用强度存在明显差异,方铅矿、闪锌矿发生强烈氧化分解,而与黄铁矿的相互作用则较弱。这种差异可能与矿物晶体结构有关,在多种矿物并存的情况下,可能发生了原电池反应,作为阴极的黄铁矿受到保护,而作为阳极的闪锌矿、方铅矿的氧化作用得到促进,总体上表现为A.f对矿石硫化矿物的选择性作用。     

硫化物矿物的表面反应及其在矿山环境研究中的应用

硫化物矿物的表面反应机理决定了以硫化物矿物为主的尾矿的重金属释放、吸附、解吸机制，其反应动力学与矿山环境污染程度存在内在联系。本文系统介绍了硫化物矿物的表面反应研究现状，包括反应机理、表面结构、表面位、反应产物、反应速率等，并指出了有待进一步研究的几个问题。     

Geochemical modeling of arsenic sulfide oxidation kinetics in a mining environment

Arsenic sulfide (AsS (am), As₂S₃ (am), orpiment, and realgar) oxidation rates increase with increasing pH values. The rates of arsenic sulfide oxidation at higher pH values relative to those at pH∼2 are in the range of 26-4478, 3-17, 8-182, and 4-10 times for As₂S₃ (am), orpiment, AsS (am), and realgar, respectively.Numerical simulations of orpiment and realgar oxidation kinetics were conducted using the geochemical reaction path code EQ3/6 to evaluate the effects of variable DO concentrations and mineral reactivity factors on water chemistry evolution during orpiment and realgar oxidation. The results show that total As concentrations increase by ∼1.14 to 13 times and that pH values decrease by ∼0.6 to 4.2 U over a range of mineral reactivity factors from 1% to 50% after 2000 days (5.5 yr). The As release from orpiment and realgar oxidation exceeds the current U.S. National Drinking Water Standard (0.05 ppm) approximately in 200-300 days at the lowest initial dissolved oxygen concentration (3 ppm) and a reactivity factor of 1%. The results of simulations of orpiment oxidation in the presence of albite and calcite show that calcite can act as an effective buffer to the acid water produced from orpiment oxidation within relatively short periods (days/months), but the release of As continues to increase.Pyrite oxidation rates are faster than orpiment and realgar from pH 2.3 to 8; however, pyrite oxidation rates are slower than As₂S₃ (am) and AsS (am) at pH 8. The activation energies of arsenic sulfide oxidation range from 16 to 124 kJ/mol at pH∼8 and temperature 25 to 40°C, and pyrite activation energies are ∼52 to 88 kJ/mol, depending on pH and temperature range. The magnitude of activation energies for both pyrite and arsenic sulfide solids indicates that the oxidation of these minerals is dominated by surface reactions, except for As₂S₃ (am). Low activation energies of As₂S₃ (am) indicate that diffusion may be rate controlling.Limestone is commonly mixed with sulfide minerals in a mining environment to prevent acid water formation. However, the oxidation rates of arsenic sulfides increase as solution pH rises and result in a greater release of As. Furthermore, the lifetimes of carbonate minerals (i.e., calcite, aragonite, and dolomite) are much shorter than those of arsenic sulfide and silicate minerals. Thus, within a geologic frame time, carbonate minerals may not be present to act as a pH buffer for acid mine waters. Additionally, the presence of silicate minerals such as pyroxenes (wollastonite, jadeite, and spodumene) and Ca-feldspars (labradorite, anorthite, and nepheline) may not be important for buffering acid solutions because these minerals dissolve faster than and have shorter lifetimes than sulfide minerals. However, other silicate minerals such as Na and K-feldspars (albite, sanidine, and microcline), quartz, pyroxenes (augite, enstatite, diopsite, and MnSiO₃) that have much longer lifetimes than arsenic sulfide minerals may be present in a system. The results of our modeling of arsenic sulfide mineral oxidation show that these minerals potentially can release significant concentrations of dissolved As to natural waters, and the factors and mechanisms involved in arsenic sulfide oxidation warrant further study.     

西范坪斑岩铜矿的次生富集作用研究

通过对3000余米岩芯的观察研究。发现西范坪斑岩铜矿床存在完整的氧化带，氧化剖面由上向下可以分为氧化带，次生富集带和原生带。原生矿石的裂隙越发育，原生矿化强度越大，则其次生富集作用越发育。应用质量平均方法计算了氧化过程中铜的迁移规律，提出在次生富集作用中铜队了发生垂向（由上向下）迁移外，也存在侧向迁移（带入或带出）。在矿床中部，由于铜的垂向富集和侧向带入而形成富矿石和厚大矿体，因此次生富集对西范斑岩铜矿床富矿体的形成起到了重要的作用。     

硅藻土、石英砂和钾离子促进微生物转化酸性矿山废水中亚铁成次生矿物的研究

嗜酸性氧化亚铁硫杆菌(Acidithiobacillus ferrooxidans)能够在低pH值条件下,迅速将Fe2+氧化并产生大量次生羟基硫酸铁沉淀,从而除去水中可溶性Fe2+。这为富含Fe2+的酸性矿山废水(acid mine drainage,AMD)处理提供了新的思路。本文从晶种刺激和阳离子诱导两个方面,分别研究了固定化载体(硅藻土、石英砂)和具有强诱导能力的成矾离子(K+)对微生物转化酸性体系中Fe2+成次生矿物的影响。结果表明,3种材料均有明显促进可溶性Fe2+向次生矿物转化的作用,且总铁(TFe)沉淀率与3种材料的添加量呈正相关关系。在起始Fe2+浓度为160mmol/L,硅藻土、石英砂和钾离子最大添加量分别为10 g、10 g和80 mmol/L时,经过72 h反应后,TFe沉淀率分别比对照增加了8%、24%和20%。矿物中的Fe、K和S元素含量与溶液中的起始K+浓度有非常密切的关系,随着K+浓度的增大,矿物中的K和S含量逐渐增加,而Fe含量则相应减少。     

Geochemical and mineralogical aspects of sulfide mine tailings

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.     

刚果（金）如瓦西铜-钴矿床表生成矿过程及其勘探意义

中非成矿带刚果（金）如瓦西（Ruashi）铜-钴矿床经历了表生成矿作用,但其研究薄弱。在野外地质调查、室内矿物学观察和矿山生产勘探的基础上,对如瓦西铜-钴矿床的表生分带组构与次生富集规律进行研究。结果表明,该矿床原生矿体由黄铜矿、斑铜矿、硫铜钴矿等含铜硫化物矿物组成,矿石品位铜在1%~2%、钴在0.1%~0.3%范围内。矿床在近地表发生表生氧化作用后,上部形成了氧化带,可进一步划分为3个亚带：（1）完全氧化亚带;（2）淋滤亚带;（3）次生氧化物富集亚带。上部完全氧化亚带发育富钴氧化物堆积体“矿帽”（钴品位在1%~3%,部分可达12%）,淋滤亚带几乎不含铜、钴金属矿物,次生富集氧化物亚带由孔雀石、硅孔雀石、蓝铜矿、胆矾、水胆矾等氧化物矿物和碳酸盐矿物组成,矿石品位铜在5%~10%、钴在0.8%~1.0%范围内,相对原生矿石富集了3~5倍。下部为次生硫化物富集带,出现蓝铜矿、辉铜矿等次生硫化物矿物,矿石品位铜在3%~5%、钴在0.3%~0.8%范围内,相对原生硫化矿富集了1~3倍。综合分析认为,如瓦西铜-钴矿床表生成矿作用受岩石地层、地质构造和地下水等因素的控制,次生富集作用明显提高了矿石品位和矿床开发价值,形成了氧化物富铜-钴矿、硫化物富铜-钴矿和碳酸盐岩接触带附近的氧化物富铜矿及黑色富钴矿等类型的高-特高品位矿体。经勘探验证,在矿区深边部新揭露高品位矿石资源量256万吨,平均品位铜为3.68%、钴为0.44%,可采储量143万吨,平均品位铜为3.53%、钴为0.32%。该研究可为矿区及区域同类型矿山硫化矿演化成氧化矿的表生富集过程及深边部找矿预测提供科学依据。     

A study on the distribution characteristics and existing states of cadmium in the Jinding Pb-Zn deposit,Yunnan Province,China

The distribution characteristics and existing state of cadmium in the Jinding Pb-Zn deposit were studied. It was discovered that Cd was mainly distributed in sphalerite as an isomorphic impurity. There was a good correla-tion between Cd and Zn in the primary ore. With the oxidation and resolution of pyrite, sphalerite, sulfide, and etc., many secondary minerals, such as colloform sphalerite and smithsonite, were formed. The distribution of Cd is not symmetrical, and enrichment and dilution were observed in partial area of the oxidation zone in the deposit. Cd, except in external pore space or cracks of secondary minerals as independent minerals, such as greenockite, was mainly distributed in sphalerite as an isomorphic impurity in the secondary sphalerate and smithsonite in the oxida-tion zone. The research showed that Cd showed a very strong active transfer ability in the oxidation process, not only indicating that supergene leaching might be the main reason for Cd enrichment in some Pb-Zn deposits, but also reflecting that Cd was easily mobilizeed and transferred to pollute ore areas in the oxidation process. Furthermore, Cd in oxidation ore was more easily mobilized and transferred to induce bad hazards for ore areas with the effect from AMD which was produced from oxidation of sulfides.     

Hydrogeochemistry and microbiology of mine drainage: An update

The extraction of mineral resources requires access through underground workings, or open pit operations, or through drillholes for solution mining. Additionally, mineral processing can generate large quantities of waste, including mill tailings, waste rock and refinery wastes, heap leach pads, and slag. Thus, through mining and mineral processing activities, large surface areas of sulfide minerals can be exposed to oxygen, water, and microbes, resulting in accelerated oxidation of sulfide and other minerals and the potential for the generation of low-quality drainage. The oxidation of sulfide minerals in mine wastes is accelerated by microbial catalysis of the oxidation of aqueous ferrous iron and sulfide. These reactions, particularly when combined with evaporation, can lead to extremely acidic drainage and very high concentrations of dissolved constituents. Although acid mine drainage is the most prevalent and damaging environmental concern associated with mining activities, generation of saline, basic and neutral drainage containing elevated concentrations of dissolved metals, non-metals, and metalloids has recently been recognized as a potential environmental concern. Acid neutralization reactions through the dissolution of carbonate, hydroxide, and silicate minerals and formation of secondary aluminum and ferric hydroxide phases can moderate the effects of acid generation and enhance the formation of secondary hydrated iron and aluminum minerals which may lessen the concentration of dissolved metals. Numerical models provide powerful tools for assessing impacts of these reactions on water quality.