空区处理与残矿回采对围岩及地表影响的数值模拟分析

为了提高矿山企业开采的生产效益及确保施工中设备人员的生命财产安全,采用现场声波测试试验与室内物理力学试验得出的力学参数,应用FLAC3D数值模拟软件,在空区顶板-矿柱体系简化为弹性矩形薄板-H-K体流变力学模型的基础上,分析空区处理与残矿回采对围岩及地表的影响规律。结果表明:矿区三中段充填回采过程中压应力最大值出现在Ⅲ-10开采之后,右帮壁形成了9. 8 MPa的压应力集中区;拉应力区域主要存在于充填体内,且大部分拉应力超过了充填体抗拉强度幅值0. 12 MPa;地表移动带范围内垂直方向位移保持在0～1 mm。实际施工中应采取加强充填体强度达0. 27 MPa以上或保留部分矿体支撑顶板等措施确保回采安全。     

The nature and significance of public exposure to arsenic: a review of its relevance to South West England

In South West England, more than two hundred years of intensive exploitation of metalliferous ore deposits, combined with the natural processes of pedogenesis from mineral-rich parent rocks, has resulted in the creation of a aignificant area of arsenic-contaminated wastes and soils. The scale of arsenic dispersion by natural and anthropogenic processes is such that 722 km² of land contains concentrations of arsenic in excess of 110 g g^–1, more than twice the maximum that might be expected in a normal soil.The general rationale for the clean-up of derelict and contaminated mining sites often includes aesthetic factors and the desirability of preventing the dispersion of contaminants beyond the site boundaries. Only in extreme cases is public health directly invoked as justification for remediation. In South West England, if arsenic constitutes a genuine threat to the public, an increased rate of site remediation would be justified. The primary purpose of this review is to establish whether or not widespread arsenic contamination (principally of soils) has any measurable effects on public health in South West England, and how this might affect current contaminated site remediation policy. The review is based on data from previous research in the region, and other relevant international studies of mining and smelting communities, and other populations exposed to elevated arsenic concentrations. The literature reviewed also includes the determination of the extent and sources of contamination, and pathways between source and man.While the contamination of potable waters in some countries has led to measurable health effects, this scenario has not yet been identified in South West England, and there is little reason to believe that significantly contaminated potable water supplies would escape detection for extended periods of time under the current monitoring regime.In relative terms (based on both globaland local data), one of the most significant links between contaminated soils and humans appears to be contaminated food stuffs. In absolute terms, such exposure is low due to the natural constraints on arsenic uptake by herbage, cereal crops and vegetables, and the food chain does not appear to have been significantly compromised in South West England. Chronic health effects are unlikely as excessive arsenic concentrations in locally grown food crops remain rare.With the problems of confounding medical and social factors, it is not surprising that studies in South West England have failed to identify chronic exposure to arsenic at very low concentrations as a significant health risk. Those studies that indicate otherwise do not stand up to close scrutiny. It appears that the number of additional deaths arising from the widespread arsenic contamination in South West England is small. The relative benefits of a costly statistical study to actually determine the number of additional deaths might be considered minimal, but one major area could benefit from further studies: the sensitivity of certain population sub-groups to environmental arsenic exposure. Of particular interest are children, for whom significant exposure to arsenic via soil ingestion may be occurring.Based on available information, there appears to be no justification for a large programme of site remediation. Resources should, however, be expended on enlightening the general public, and private and governmental organisations as regards the gap between the perceived and actual significance of arsenic contamination in South West England.To whom correspondence should be addressed.     

初论元素富集成矿的地球化学机理—以岩浆热液矿床的形成为例

元素富集成矿的过程实质上是元素在地球不同圈层和不同相以及不同集合体之间分配的结果。元素的富集起始于地球形成的初期。对于大多数金属成矿元素 ,地壳特别是上地壳是大多数矿石和矿胎的储库 ,地壳丰度是元素富集成矿的物质基础。元素在地质体系演化共存相间的分配是元素富集成矿的关键过程。对于以侵入体为中心的热液矿床的形成 ,岩浆部分熔融、结晶分异、液态分离、挥发分分离以及气液相不混溶等过程能够导致金属元素最终达到矿石级的富集。挥发分则是元素富集成矿的重要制约因素     

贵州独山锑矿田地质地球化学特征和构造动力热液成矿

独山锑矿田位于独山箱状背斜核部近倾伏端,矿床、矿体的产出严格受断裂控制,其半坡式锑矿呈脉状产于下泥盆统、志留系碎屑岩的陡倾斜断裂中;其巴年式的锑矿呈层状产于中泥盆统碎屑岩与碳酸盐岩之间的层间滑动带中。成矿温度低,矿石组分和围岩蚀变简单,锑主要来源于下伏地层,硫主要来源于赋矿地层．成矿流体主要为大气降水,构造动力成矿作用导致锑矿床的形成,矿床类型为一典型的构过动对热液矿床。     

从桂西北隆或金矿的地质地球化学特征看微细粒浸染型金矿的可能成因

在区域微细粒浸染型（卡林型）金矿床物源、成矿作用和构造控矿等方面研究的基础上，重点讨论了桂西北隆或金矿的地质地球化学特征。研究结果表明，该金矿店的穹隆构造、深断裂控矿、多层位赋矿和围岩蚀变等矿床地质特征，在滇黔桂三省区交界地区微细粒浸染型金矿中既具有普遍性，又表现出特殊性，其原生成矿硅质流体可能主要直接来自深部岩浆源分异作用，但由于是在地壳中成矿．不可避免地受到部分地层的物质和流体的混杂，因而属于地慢上隆－构造岩浆活化分异－深大断裂导矿－次级断裂、背科控矿－交代充填成矿的中偏低温热液金矿床。     

炼铁上料系统除尘设计体会点滴

就炼铁高炉矿槽除尘系统的方式，提出了一些革新的措施，涉及到阀门、吸气罩、风幕及控制方法等     

新疆赛都糜棱岩型金矿的矿石矿物学特征

本文首次详细论述了赛都糜棱岩型金矿的矿石类型、矿石组构和金属矿物的特征，对金矿物特征和金的赋存状态作了详细描述，并在矿石矿物学分析基础上提出了该金矿的矿化阶段。     

开发沸石矿用于农业的经济评价

我国沸石矿资源丰富。开发利用沸石矿于农业,可增产粮食400亿公斤,加上节约化肥和用作饲料添加剂等方面,年经济效益为496.25亿元。因此,开发利用沸石矿于农业具有重大的经济意义,从促进我国粮食生产上新台阶的角度考虑,则具有重大的战略意义。     

粤东一个类型独特的锡矿床

作者对西岭凤地山锡矿床的成矿地质条件,特别是火山构造、岩浆演化与成矿的关系进行了研究,认为:西岭锡矿是一个与火山侵出相碎斑熔岩时、空、成因关系密切的次火山热液脉状锡矿床。根据西岭锡矿的地质环境和成矿物理化学条件、矿质、水介质来源建立了理想的成矿模式。进而指出粤东斑岩锡矿的远景。西岭锡矿类型的确定,对粤东和赣南火山岩地区锡矿普查具有重要意义。     

三门火山盆地的层状矿床及其与盆地形成演化的关系

浙江三门中生代火山——沉积盆地的形成演化可分四个阶段。每一阶段均伴产有不同成因和各具特色的金属矿床,显示了陆相火山作用较为完整的成矿体系。其中层状矿床具有同生和后生的双重特征,多成因,多来源,是较典型的火山沉积——后期热液迭加改造型矿床。本文着重介绍它的主要特征及盆地的形成演化对火山成因矿床的控制。