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）.     

赣东北金矿成矿地质特征与找矿方向

赣东北地区金矿资源丰富,成矿地质背景优越,金矿床类型多样,有6类16型,其中主要工业类型为次火山斑岩型伴生金矿、韧性剪切带糜棱岩型金矿、剪切石英脉带蚀变岩型金矿和冲积型砂金矿。这四种工业类型中韧性剪切带糜棱岩型金矿和剪切石英脉带蚀变岩型金矿均有较好的勘查前景,尤以后者找矿潜力巨大。在叙述赣东北地区金矿成矿地质背景、金矿类型划分、金矿主要工业类型和典型金矿床实例的基础上,阐述了金矿成矿规律,提出了今后勘查的主攻矿床类型,找矿远景区,预测并指明了主要金矿类型的未来找矿潜力。为赣东北地区金矿的进一步勘查与开发,提供一些有益的参考和启示。     

金、银等成矿元素的构造地球化学行为

扬子与华夏地块间发育一条近东西向展布的巨型板块缝合带—华南中部复合混杂岩带,由北东向、近东西向、北北东向三组方位的次级韧性剪切带分支、复合成“网格状”构造阵列。对其次级北东向剪切带(进贤—婺源韧性剪切带)进行的构造地球化学剖面研究发现从剪切带边部至中心,随着剪切程度的逐渐增强,金、铜元素含量逐渐增高,锌元素含量逐渐降低,铅、银元素含量变化不明显、略有降低的趋势;金元素有两个峰值点,一个出现在韧性剪切最强的糜棱岩中,另一个出现在叠加于早期韧性剪切糜棱岩化岩石之上的晚期脆性破裂张性构造角砾岩中,说明韧性剪切及叠加在韧性剪切之上的脆性破裂均有利于金的富集成矿,从而为赣东北地区寻找金矿指明了方向,并为金的成矿构造地球化学理论研究积累了新的素材。     

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.     

深部找铀及湘南-桂北地区深部找铀潜景分析

概述了国内外深部找矿的研究成果,指出深部找矿是当今发展的趋势。国内外重大矿产的成功发掘,其深度均在千米以上,铀矿化垂向分布深度可达4 km以上。综合介绍了国内外勘查深大矿床的特点和条件,认为岩石-构造条件是深部矿化定位的重要因素,复式岩体、成矿系统的垂向变化、构造地球物理-地球化学异常模型是深部找矿的关键依据。综述了中国南方湘南—桂北地区深部找铀的有利地质构造条件和潜力,成矿流体是该区铀矿化的根源,白垩—第三纪重大地质事件是该区深部铀成矿的重要前提,重大地质事件引发的NE-NNE,NW向深大断裂及断陷盆地是铀矿化赋存的重要场所和勘查靶区。在已知铀矿田、成矿带勘查范围基础上,在该区进行深部探索将会获得重大突破。探讨了湘南—桂北地区深部找铀的勘查思路和方法。     

下庄铀矿田337矿床成矿流体稀土元素示踪

337铀矿床位于下庄矿田东缘,区内发育近EW向、NNE向构造裂隙群及NW向辉绿岩和正长岩脉体,发育以碱性为主的多种围岩蚀变。区内矿床主要赋矿围岩的稀土元素特征属壳源型。矿石内金属矿物以沥青铀矿为主,矿石的LREE/HREE比值为3.25,Sm/Nd比值平均为0.307,Ce/Yb比值为7.127,这些数据都显示出成矿流体具有较深来源。矿石较围岩亏损稀土元素尤其是轻稀土元素,稀土元素分布模式平缓,与幔源辉绿岩特别是与正长岩的稀土元素分布模式相近,负铕异常比围岩更为强烈,反映成矿流体的来源具有幔源性。结合区域地质特征,可以认为337矿床成矿流体来源具有幔源性质。     

华东铀资源潜力分析及危机矿山接替资源勘查工作设想

华东地区铀成矿条件良好,铀资源丰富,经过近50年的铀矿勘查,探明了大量的铀资源/储量,目前全国保留的八大铀矿山中华东有三个,每年给国家提交一定量的铀资源。随着我国核电的快速发展,铀资源的需求日趋紧迫,立足铀资源国内的原则必须继续寻找南方硬岩型铀资源。作者在总结调查报告成果的基础上,从全局的高度出发,分析了华东铀资源开采、利用现状及铀资源潜力,在实地考察华东三大铀山铀资源开采、利用情况的基础上,初步分析了资源危机程度,提出了华东铀矿山接替资源勘查工作意见。     

香炉山地区找矿前景初步分析

通过对香炉山地区成矿控制因素分析,认为香炉山特大型钨矿外围具备找大矿的条件,并依据成矿控制主要因素在找矿远景区的具体体现,提出了在徐家岭、张天罗、大岩下等多处具有较好的找矿远景区。对张天罗、徐家岭及大岩下等较重要的找矿前景区进行详细叙述。     

长坡区锡多金属矿床地质特征与成矿条件分析

长坡区锡多金属矿床位于大厂锡多金属矿田的西矿带,它是在地层、断裂构造和岩浆岩“三位一体“作用下形成的,地层是基础条件,断裂构造起了主导作用,岩浆提供热源以及可能提供了液源甚至矿质.因此,今后找矿中,更应关注断裂构造的研究.