我国藻菌生物成因的金矿研究

生物成矿作用分为生物直接成矿作用和生物间接成矿作用,生物直接成矿作用的标志结构为生物有机胶体结构。生物间接成矿作用的标志结构为“矿交代生物”结构,我国陕西二台子－半仓沟金矿,四川东北寨金矿、川甘拉尔玛金矿和云南金厂金矿等均为典型为实例,矿石中普遍含有多种金属矿物生物结构,还含多种生物有机组分。成矿物质具有多源性特征,硫同位素具混合型特征,矿床成型机制可与“人工碳吸附系统”聚金机制相类比,含金层位可     

磷块岩研究进展与磷块岩生物成矿说

近十年来,我国磷块岩的研究以沉积学的发展为先导,取得了长足进展。十年迈出两大步:第一步是由化学沉积说向物理富集成矿说的转变;第二步是生物成矿说的发展。业已在我国南方晚震旦-早寒武世各主要工业矿床的磷块岩中发现了大量多种形态的原核生物的细菌到真核生物的真菌等磷质微生物以及藻类和小壳动物化石(后者产于早寒武世磷矿中),它们是构成磷块岩的主要组分。磷块岩实际是一种特殊的生物岩。本文论述了磷块岩的生物成矿作用、生物聚磷机理,并从磷块岩岩石的生物特点、化学成分的生物特点、红外吸收光谱以及稀土元素组成的生物特点等方面,论述了磷块岩的生物成因。同时阐述了磷质生物繁衍的环境条件与磷块岩形成环境之间的内在联系,以及磷质生物的最佳繁衍场所与磷块岩成矿古地理单元的一致性,这种“生物繁衍场”与成磷古地理单元可称之谓“陆缘坻”。     

安徽铜陵凤凰山铜（金）矿床矽卡岩型与斑岩型复合成矿作用流体研究

凤凰山铜（金）矿床产于燕山晚期花岗闪长岩及石英二长闪长斑岩与三叠系碳酸盐岩的接触带，先后包括矽卡岩型和斑岩型两期矿化，并可细分为9个成矿阶段。矿石中广泛出现角砾状和细脉状、网脉状构造。流体包裹体特征及显微冷热台测温资料表明，成矿流体存在过沸腾和局部超高压等现象。两个成矿期都经历了从高温高盐度向低温低盐度的转变，成矿溶液的主要成分也由钾钠型变成了钠钙型。来源于岩浆热液的早期含矿流体与来自围岩的地下水热液的混合可以解释成矿流体的这种演化。     

北山地区岩浆活动与金矿成矿作用关系探讨

北山地区金矿床的产出与花岗岩类侵入岩之间具有明显的空间分布关系，金矿床的形成时代与区域岩浆活动在时间上存在明显的耦合关系。研究结果表明，北山地区大规模的金成矿作用主要与塔里木、哈萨克斯坦和西伯利亚三大板块之间的碰撞对接及其后陆内活化诱发的大规模岩浆侵入-喷发活动有关。     

含金剪切带蚀变特征及其与金成矿的关系——以新疆天格尔金矿带为例

含金剪切带剪切变形过程中构造、流体-岩石相互作用导致系统内组分的迁移和再分配，这些过程控制着含金剪切带内蚀变特征及其金的成矿作用。在含金剪切带脆-韧性变形域内，成矿层次从深到浅矿石类型由蚀变糜棱岩型向石英脉型过渡，矿床成因类型由韧性剪切带型向蚀变破碎带型过渡，是主期剪切成岩成矿过程中不同时空演化阶段的产物。     

个旧矿集区锡铜多金属多因复成成矿机制

滇东南地区大地构造演化经历了前地槽及地槽阶段、地台阶段和地洼阶段。地槽演化阶段即有锡的初步富集；地台演化阶段的早期即初“定”期，由于受基底活动余波的影响，地壳仍有较大的活动性，在滇东南一带产生了强烈的断拉谷运动及与之伴生的海底火山成矿作用，造成锡铜多金属的再次富集；当壳体演化至燕山期地洼阶段，早期北东向断拉谷系统再次活化，形成大规模的深部壳源重熔岩浆，岩浆重熔及上侵定位过程中同熔或萃取了大量的深源锡铜等成矿元素，在构造有利部位对先成矿体或矿化体进行再造和叠加富化，并形成了一系列具后生成矿特征的矿化类型。文章阐述了个旧矿集区锡铜多金属成矿大地构造背景和多因复成成矿机制。     

吐哈盆地铀成矿远景区构造型式

吐哈盆地是我国重要的地浸砂岩型铀矿成矿盆地。经过对吐哈盆地的综合地质调查、钻探评价和资料分析研究，预测出西南缘艾丁湖斜坡带、大南湖、沙尔湖、三道岭地区和塔克泉构造带为地浸砂岩型铀成矿远景区。铀成矿远景区由于构造作用的相对特殊性和差异性，可划分出断-超褶曲式、断-隆式、断-阶式、斜-断式（单斜式）4种构造型式，这4种构造型式对铀成矿作用过程产生不同制约。综合分析认为艾丁湖斜坡带、大南湖地区地浸砂岩型铀矿成矿构造条件最好：三道岭、沙尔湖虽具备局部稳定构造斜坡环境，但受构造影响，潜力有限。     

Associations and mobility of uranium in soils near a depleted uranium （DU） weapons testing site, SW Scotland

Natural uranium has three isotopes, ^238U, ^235U and ^234U, with natural abundances of 99.27 atom %, 0.72% and 0.0055%, respectively. Only ^235U is fissile and the production of nuclear fuel and nuclear weapons involves enrichment of uranium in ^235U. This process also results in separation of ^234U from ^238U, leaving depleted uranium （DU）, with typical ^234U/^238U and ^235U/^238U activity ratios of about 0.19 and 0.013, respectively, as a waste product. The high density, high melting and boiling points and chemical stability of uranium and the availability of DU in relatively pure form mean that DU has many uses, including armour-piercing munitions. Such munitions have been developed in the UK since the 1960s and testing has been carried out by the Ministry of Defence （MoD） at firing ranges such as Dundrennan, SW Scotland and Eskmeals, NW England. The firing of DU munitions can result in the dispersion of DU and its combustion products （oxides） as aerosols or as larger fragments, with the potential for human exposure either directly at the site of detonation or via post-depositional migration in the environment. The aim of this work was to investigate the potential environmental mobility of DU by characterizing the associations of U in soil porewaters with increasing distance from a firing site. To this end, several soil cores located down-wind of the firing site at Dundrennan, near Kirkcudbright, SW Scotland, were collected in May 2006. These were sectioned on-site into 1- or 2-cm depth intervals and porewaters were isolated by centfifugation （10 minutes; 8873 g） on return to the laboratory. Following filtration through 0.2-micron cellulose nitrate filters, the porewaters were analyzed by ICP-QMS （U concentration） and ICP-OES （Fe, Al, Ca, Mg, Mn concentrations）. Sub-samples were also subjected to centrifugal ultrafiltration （100, 30, and 3 kD） and to gel electrophoretic fractionation （agarose; 0.045 M Tris-borate; 20 mA, 30 minutes）. Results showed that U was present at up to 4 μg/L in the soil porewater and that the associations of U varied with sample location and soil depth.     

Synergistic effect of combining sulfate reducing bacteria and zerovalent iron permeable reactive barriers on the treatment of groundwater rich in uranium, sulfate and heavy metals

Uranium processing and mining activities that generate many contaminants, such as high concentrations of U （VI）, sulfate and heavy metals （Zn, Cu, Ni, etc）, may pose a serious threat to the groundwater resources. In recent years, considerable research has been conducted respectively on two kinds of permeable reactive barriers （PRB）, including zerovalent iron （ZVI） and sulfate reducing bacteria （SRB）, for in-situ removal of these pollutants from groundwater. However, little investigation has been carried out on the potential benefits of bioaugmenting ZVI barriers to enhance the elimination of the pollutants by combining ZVI with SRB systems. The main goal of this study was to conduct batch and column experiments to determine whether the combination of SRB and ZVI can function synergistically and accelerate the rate of pollutant removal. The results of anaerobic batch experiments demonstrated that although the integrated ZVI/PRB system itself has no ability to reduce and remove sulfate directly, SRB can utilize hydrogen gas produced during the slow process of ZVI corrosion as an electron donor to raise biomass yields significantly and accelerate reductive sulfate removal. In particular, ferrous cations produced as the byproduct of ZVI corrosion process reacted with hydrogen sulfide from sulfate reduction and formed iron-bearing sulfide precipitates, which can stimulate the growth of SRB and promote sulfate removal activity by eliminating the biotoxicity of hydrogen sulfide. It was also shown that secondary mineral products （pyrite/ferrous sulfide） formed as a consequence of microbial sulfate reduction and ZVI corrosion process can enhance the microbial precipitation of soluble U （VI） as insoluble uraninite（uranium dioxide）.     

大湾铀矿田铀-镭平衡系数及迁移富集特征研究

从分析大湾铀矿田各矿床(点)的铀镭平衡系数变化特征出发,结合放射性同位素比值特征分析铀镭迁移富集行为,指出了各矿床(点)氧化带的深度,以了解各铀矿床(点)潜在的工业价值.