安徽省枞阳县拔茅山铜矿地质特征

产于庐枞中生代火山岩盆地中的石英大脉状铜矿受放射状火山构造控制。枞阳县拔茅山铜矿位于庐枞盆地南部,为细脉浸染型铜矿,降低边界品位圈定的矿体具有带状斑岩铜矿特征。依据庐枞地区的铜矿矿体形态垂向分带模式,指出寻找带状斑岩铜矿的方向。     

吉林五凤─五星山低硫型浅成热液金矿床地质特征与成矿条件

五凤—五星山金矿床属中生代陆相火山岩低流型浅成热液型金矿床。侏罗系上统金沟岭组火山岩为其主要矿源层，矿体受火山机构的断裂、裂隙和次火山岩脉内外接触带控制。碱长花岗岩侵入金沟岭组底部，为金矿形成提供了热源。成矿作用主要在低压、中性介质和弱氧化、超浅成条件下进行。金矿一般富集于矿体上部；矿体转弯、膨大处及分支复合处；强冰长石绢云母硅化蚀变岩中；含细粒黄铁矿的方解石石英脉；辉银矿集中地段。     

新疆托里齐求Ⅰ号金矿控矿构造研究

齐求Ⅰ号金矿产于中晚石炭统海相基性火山喷发沉积岩中 ,为典型的中温热液矿床 ,以石英脉型金矿为主 ,蚀变岩型金矿为辅。矿化受断裂控制 ,系火山机构与断裂构造复合控矿 ,环状构造内北西向断裂矿化较好 ,矿脉向西南深部有归并趋势。     

新疆托里齐求Ι号金矿控矿构造研究

齐求Ⅰ号金矿产于中晚石炭统海相基性火山喷发沉积岩中,为典型的中温热液矿床,以石英脉型金矿为主,蚀变岩型金矿为辅.矿化受断裂控制,系火山机构与断裂构造复合控矿,环状构造内北西向断裂矿化较好,矿脉向西南深部有归并趋势.     

山西堡子湾金矿区成矿流体场特征与隐伏矿床定位预测

综合运用遥感微差信息处理技术、水系沉积物X荧光测量和地表基岩伽玛能谱测量方法研究了山西堡子湾金矿的成矿流体场 ,发现主要的矿化蚀变带呈NW向展布 ,与含矿的NEE向角砾岩带斜交 ,表明成矿后受到一定程度的改造。矿区内存在着两类矿体 ,即陡倾斜的隐爆角砾岩型金矿和缓倾斜的蚀变岩型金矿 ,已知矿体和蚀变带主要受矿区南部的环形构造控制 ,该环形构造可能与隐伏岩体顶部拆离断层系统有关     

吕宋岛弧西缘浅成低温热液成矿作用——以拉拉布金矿床为例

拉拉布脉状金矿床是西必塔矿集区最典型的矿床,而西必塔矿集区脉状浅成低温热液型金矿是近年来发现的最具经济潜力的金矿床之一。金矿赋存于中新世—更新世马林丹群火山岩中,该火山岩呈零星岛状散布于斯丹岗—哥塔巴托—大姑玛线性构造活动带(SCDL)的东部,并受到安山玢岩侵入。该火山岩可分为上、下段两段。下段由安山质熔岩、英安岩、凝灰岩组成,上段为火山角砾岩和凝灰质角砾岩。拉拉布矿床的安山岩具有明显的热液蚀变,属于冰长石—绢云母型金矿化。金是在pH值近中性的浅表环境中由于热液沸腾并伴随流体的混合沉淀而成,通常富集于标高30~200 m之间。金的富集有4个阶段(1)形成角砾岩之前的围岩蚀变作用;(2)热液角砾岩的形成;(3)形成角砾岩后的围岩蚀变作用;(4)金矿形成。     

西藏山南错那县吉松铅矿床地质特征及成因探讨

吉松铅矿床位于喜马拉雅板片拉轨岗日陆隆壳片南部,属拉轨岗日成矿带.三年来的勘查成果显示,该矿床成矿地质条件较好,北东向断裂带及其次级断裂为主要的导矿和容矿构造,强蚀变中基性岩脉与炭质板岩的外接触带部位,特别是硅化和绿帘石化地带是矿体有利的富集部位,围岩蚀变强弱与矿化有着密切关系,矿床为硅化破碎带中低温热液交代型矿床,具有较好的找矿前景.     

江西省会昌县淘锡坝大型锡矿床构造控矿机制探讨

淘锡坝锡矿床是近年探明储量达大型的锡矿床,是一种新的锡矿类型-隐爆层间裂隙带型。文章介绍了该矿床的地质特征和矿化特征,对矿区的构造进行了重点解剖,对构造控矿机理进行了探讨,提出火山机构及北东向断裂是矿区的控岩构造,控制了白垩纪成矿花岗岩体的侵入就位。而火山岩中大范围的隐爆层间裂隙带是良好的容矿构造,矿体赋存其中呈似层状,局部膨大形成厚达数十米的"锡矿包"。通过研究构造与矿化富集的内在联系,总结了该矿床的成矿规律。     

福建省梅仙式块状硫化物矿床

梅仙式铅锌矿床是在大陆裂谷环境下形成的，有明显的块状硫化物矿床特征。矿化受震旦系龙北溪组绿片岩控制。矿体里似层状，与围岩产状一致。绿片岩原岩是一套含板内拉斑玄武岩的火山沉积建造。矿物组合和 Ｚｎ／Ｐｂ比值有分带性。层状矿体下盘有脉状、网脉状矿化和蚀变带。矿石有特征的结构构造。硫以幔源为主，铅是幔壳混合成因，矿液以海水成因为主．可能有少量雨水、岩浆水等渗入，反映物质的多来源和成矿受多种地质事件的叠加改造。本式矿床可与火山岩容矿型的加拿大新不伦瑞克省的块状硫化物矿床类比，也可作为广义华南型的一个亚型。     

北武夷梨子坑火山盆地流纹斑岩与铅锌矿的成因关系

梨子坑火山盆地位于北武夷中生代月凤山—梨子坑火山岩带东段,已知铅锌(铜、银)矿体或矿化呈细脉-浸染型、脉状,产于流纹斑岩脉的内外接触带及其外侧围岩中,发育钾化、绿泥石化、硅化、绿帘石化等围岩蚀变。地球化学特征显示流纹斑岩为钙碱性系列,岩石具有高SiO2、富碱、高K2O、高钙铁、低镁、K2O/Na2O值偏高的特点,为强过铝质岩石。w(ΣREE)值为76.28×10-6～222.54×10-6,ω(ΣLREE/ΣHREE)比值较大,为4.08～12.30,属于轻稀土元素富集型。成矿流纹斑岩形成于137±2.1Ma(SHRIMP锆石U-Pb法)～138.8±1.4Ma(LA-MC-ICPMS锆石U-Pb法),属早白垩世。铅锌矿属于次火山斑岩脉型铅锌(银铜)成矿系列,划分为次火山斑岩脉型和次火山热液破碎带型两种矿床成因类型。     

青春 责任 梦想 行动 2015年千名青年环境友好使者夏令营侧记

<正>"我们处在世界正在发生重大变革的时代,中国也正在实现着民族伟大复兴的关键时刻。青年人要承担什么责任?""我们应该团结更多的青年人,向全社会积极宣传环保理念,保护我们共同生存的家园。"一名青年使者刚刚回答完贾峰主任的问题,全场响起的是掌声——雷鸣般的掌声!8月17日,2015年"千名青年环境友好使者夏令营"在成都市温江区正式开营。环境保护部宣传教育中心主任贾峰亲临现场,并为青年学子们讲授了热情     

Asbeste Arten,Entstehung, Bedeutung,Problematik

Types of asbestos are distinguished not only by structure, chemical compositon, shape of aggregates, and length and quality of fibers, but also by its formation. Though consisting of quite common elements, deposits are formed only under very special conditions. Its unique combination of properties has created over 3000 fields of application (about 70% in asbestos cement). Great efforts have been made to substitute all types of asbestos by harmless, similarly cheap and versatile synthetic fibers, owing to the unquestioned carcinogenic properties of all asbestos dusts. However, development of such fibers has not made any remarkable progress until recently. Consequently risk to workers in mining and manufactoring, consumers, outsiders, and the environment should be kept as low as possible by intensifying precautions and diminishing emissions.     

Effect of CaO on retention of S, Cl, Br, As, Mn, V, Cr, Ni, Cu, Zn, W and Pb in bottom ashes from fluidized-bed coal combustion power station

This work was conducted to evaluate whether Ca-bearing additives used during coal combustion can also help with the retention of some other elements. This work was focused on the evaluation of bottom ashes collected during four full-scale combustion tests at an operating thermal fluidized-bed power station. Bottom ashes were preferred to fly ashes for the study to avoid interference from condensation processes usually occurring in the post-combustion zone. This work focused on the behaviors of S, Cl, Br, As, Mn, V, Cr, Ni, Cu,Zn, W, and Pb. Strong positive correlations with CaO content in bottom ashes were observed（for all four combustion tests） for S, As, Cl and Br（R = 0.917-0.999）. Strong inverse proportionality was calculated between the contents of Pb, Zn, Ni, Cr and Mn and CaO, so these elements showed association to materials other than Ca-bearing compounds（e.g., to aluminosilicates, organic matter, etc.）. Somewhat unclear behaviors were observed for W, Cu, and V. Their correlation coefficients were evaluated as statistically ＂not significant＂, i.e., these elements were not thought to be significantly associated with CaO. It was also discovered that major enrichment of CaO in the finest bottom ash fractions could be advantageously used for simple separation of elements strongly associated with these fractions, mainly S and As, but also Cl or Br. Removal of5% of the finest ash particles brings about a decrease in As concentration down to 77%-80% of its original bulk ash content, which can be conveniently used e.g., when high As content complicates further ash utilization.     

珊瑚钨锡矿硅质尾矿中Cd、As、Zn、F富集迁移及环境污染

硅质尾矿在释放中性矿山废水(NMD)时所伴生的多元素复合污染问题值得重视。本文以桂东北珊瑚矿尾矿作为研究对象,通过分析该尾矿的组构、元素富集及迁移特性,筛选出主要污染元素,并探讨尾矿胶结层对元素富集迁移的影响。结果表明:(1)该尾矿中Cd、As、Zn及F富集程度较高、可交换态含量(易迁移释放量)较大,是主要的污染元素,而Cu、Pb、Tl产生污染的可能性较小;(2)胶结层对重金属具有再富集作用,但其对可交换态Cd、As(Tl)再富集明显,而对可交换态Cu、Pb、Zn再富集则不明显。胶结层中次生伊利石、石膏等胶结物趋向于吸附富集活性可交换态Cd、As。这表明该尾矿可能迁移释放出含Cd、As浓度较高的NMD。研究表明,硅质尾矿风化释出NMD的同时,可能伴生Cd、As、Zn等重金属以及F的复合污染。     

意大利的金枪鱼、箭鱼、鸬鹚以及家燕等体内的多氯萘、多氯联苯、多氯二苯-p-二恶英、多氯二苯并呋喃以及p,p''''-DDE

我们曾对从意大利收集的金枪鱼、箭鱼、普通鸬鹚以及家燕体内的p,p'-DDE、多氯联苯同类物(PCBs)、多氯二苯-p-二恶英(PCDDs)、多氯二苯并呋喃(PCDFs)以及多氯萘(PCNs)浓度进行过测量.     

The monitoring,Evaluation, reporting,verification, and certification of energy-efficiency projects

In this paper, we present an overview of guidelinesdeveloped for the monitoring, evaluation, reporting,verification, and certification (MERVC) ofenergy-efficiency projects for climate changemitigation. The monitoring and evaluation ofenergy-efficiency projects is needed to determine moreaccurately their impact on greenhouse gas (GHG)emissions and other attributes, and to ensure that theglobal climate is protected and that countryobligations are met. Reporting, verification andcertification will be needed for addressing therequirements of the Kyoto Protocol. While the cost ofmonitoring and evaluation of energy-efficiencyprojects is expected to be about 5–10% of a project'sbudget, the actual cost of monitoring and evaluationwill vary depending on many factors, including thelevel of precision required for measuring energy andGHG reductions, type of project, and amount of fundingavailable.