银山多金属矿床成矿流体稀土元素地球化学

对江西银山矿床规模不同的矿体、蚀变围岩及其原岩的稀土元素特征进行了对比研究。结果表明 ,成矿流体的稀土元素以轻稀土富集型 ,无Ce异常 ,强烈的Eu正异常而显著地区别于赋矿围岩。热液蚀变作用造成围岩的稀土总量升高 12 .1%～ 5 2 .4%,轻重稀土比值降低 ,但紧邻矿体的稀土含量则低于原岩。导致围岩稀土总量升高有两个因素 :(1)通过热液蚀变作用带入了稀土元素 ;(2 )体系主元素 (Si)质量迁移而造成稀土元素出现表观浓缩。其中以前者为主导因素。矿体的接触带及其紧邻处的蚀变围岩的REE含量明显偏低 ,主要因出现大量石英或石英 +硫化物等矿物的显微脉体 (脉幅 3～ 8μm)而被稀释 ,是一种表观亏损现象。研究结果表明 ,矿体越大 ,其围岩REE被“稀释”越明显 ,涉及的范围越大 ,REE特征可能是一种潜在有效的找矿勘探地球化学指标。     

牛仔布染整废水处理技术及应用

以贵阳纺纱厂牛仔布生产车间废水处理工程为实例,介绍了“絮凝床-迷宫沉淀”技术对含靛兰染料、淀粉和PVC浆料的染整废水处理情况。经半年的工程实际运转表明,在进水污染物平均浓度：色度、SS、COD、BOD、NH3-N分别为400(稀释倍数)、97．0mg／L、821mg／L、189.51mg／L、1．8mg／L情况下,处理效果良好,其去除率分别为97．5％、97．4％、94．0％、90．0％、58．3％,出水达到了《纺织染整工业水污染物排放标准》(GB-4287-93)一级,符合环保要求,且可以回用于绿化、冲地坪等。该技术投资和运行费用合理,操作管理方便,适合中小型纺织印染厂废水处理。     

崇义县八仙脑钨锡矿床特征

通过对八仙脑矿区的地质工作,发现本区存在破碎带-石英脉复合型、石英细脉带型、云英岩-石英细(网)脉带型等一体多型钨锡多金属矿床类型,本文对其地质特征进行了较为详细的论述,总结了区内各钨锡多金属矿床类型找矿评价的工作方法。     

贵州滥木厂铊(汞)矿床构造控矿特征及其模拟实验研究

滥木厂铊 (汞 )矿床产于NE向滥木厂鼻状背斜核部和近核部 ,并严格受控于与背斜关系密切的NE向断裂组。矿床中矿体的产出则多与层间虚脱空间有关 ,且主要产于晚二叠世龙潭组 (P2 l)和长兴组 -大隆组 (P2 c+d)。对该矿床不同部位取样并进行构造地球化学模拟实验 ,其结果表明 :成矿元素的活化和迁移与塑性变形关系密切 ,脆性变形和塑性变形的层间滑移则为矿体形成提供了有利空间 ;在应力作用下 ,导致有机质的局部富集 ,为富铊矿体的形成提供了条件。实验结果与汞铊矿体和富铊矿体主要产于晚二叠世含煤岩系有利岩石组合内的情况一致     

河南省嵩县东湾-蛮峪金矿床地质特征及找矿意义

本文通过对东湾金矿矿区的地质概况、矿床地质特征的分析研究,得出东湾金矿是岩浆热液形成的构造蚀变岩型金矿,成矿时代属燕山晚期,燕山期岩浆活动不仅提供强大的热动力条件,而且还从矿源层中携带大量的成矿物质,在构造有利部位,尤其是NNE向断裂构造部位沉淀富集成矿,总结出了找矿标志和预测了今后的找矿方向。     

陕西靖边统万城建城时期地表物质成因与自然环境

为查明距今约1600年的统万城建城时期的自然环境和该古城是否建在风沙沉积之上这一长期争议的问题,对6个钻孔剖面样品进行粒度和X-射线衍射等分析。结果表明：城墙内外地表之下均为湖泊沉积,沉积物特点与风沙沉积物显著不同,主要表现为以下五个方面：（1）沙层含有褐黄色针铁矿;（2）有多个深灰色沉积层;（3）沙层中粗砂含量显著大于风积沙层;（4）沙层中粒度成分的分选性比风积沙层明显差;（5）细粒斑点中Fe₂O₃与Al₂O₃含量比风沙沉积物高。本文获得的证据充分表明,在统万城建城前后,该区自然环境较好,普遍分布的是由湖积物组成的高平地,统万城建在湖积沙层之上。统万城建城时期基本没有发生沙漠化,沙漠化发生在建城之后的一定时期。     

某铅锌矿区农田重金属分布特征及其风险评价

为进一步探讨铅锌矿开采和冶炼地区农田重金属污染的分布特征和污染途径,以会泽县者海镇铅锌矿区周边农田土壤为研究对象,共布设496个采样点,测定表层土壤中重金属（Cd、Hg、Pb、Cu、Zn）的含量.利用自然邻点法对表层土壤中重金属含量进行插值拟合,以空间三维模型研究该地区农田土壤重金属污染特征,运用单因子指数、综合污染指数和潜在生态风险指数法对重金属污染程度进行评价,采用相关分析、主成分分析和聚类分析识别污染途径.结果表明：Cd、Hg、Pb、Cu和Zn的含量平均值（mg/kg）分别是云南省背景值的33.05、5.83、12.02、4.89和16.33倍;Cd、Hg、Pb、Zn含量空间分布表现为西北部浓度最高,且中部高于东西两侧,而Cu与此相反;单因子指数评价结果显示99.8%的土样达到Cd重度污染,其次是Cu（82.06%）、Zn（62.50%）;综合污染指数表明,研究区均处于重度污染程度,西北部尤为严重;综合生态风险评价表明,中部风险高两边低,Cd的贡献率最大占61%;相关分析结果显示,Zn、Cd、Pb、Hg之间呈显著正相关性（P < 0.01）,表明其污染途径相近;主成分分析和聚类分析表明,Cd、Hg、Pb、Zn污染途径主要与人类活动有关,Cu主要受自然因素影响,因此对该地区土壤重金属的修复和治理应综合考虑人为因素和自然因素的影响.     

某矿区农田土壤重金属潜在生态风险评价及形态分析研究

对广西某矿区农田土壤中的Cd、Pb、Zn、Hg进行潜在生态风险评价及存在形态分析.结果表明,研究区域Cd为极强危害程度,Pb和Hg为很强危害程度,Zn为中等危害程度,所有采样点位均处于很强危害程度,其中主要的贡献来自于Cd.形态分析结果表明,Cd以可交换态为主,Pb以碳酸盐态和铁锰氧化态为主,Zn以残渣态、有机结合态和铁锰氧化态为主,Hg以残渣态和有机结合态为主.次生相与原生相分布比值法与潜在生态风险评价法评价结果存在差异,两种方法的评价结果均应加以考虑.     

Utilizing vortex behaviour to minimize drift

Abstract

The ULV spray emitted from a TBM flying in a cross wind was mapped by a scanning lidar system. The fate of the spray cloud for 2 min after release from the aircraft was followed as the material was transported downwind of the flight line. Vertical scans at 6 s intervals with 1 m^‐3 resolution provided detailed insight into the entrainment of the spray into the wing‐tip vortices and ultimate release to drift or deposit. Relative concentration, dosage and deposit profiles are presented for this cross‐wind case. Vortex lifetimes were found to be significantly different for the up‐wind and downwind vortices. The majority of the near field deposit was associated with the up‐wind vortex while the drift was linked to the down‐wind vortex.     

Foliar and ground deposits of fenitrothion following aerial application over a plantation forest

Abstract

Spray deposits were measured on spruce foliage at tree canopy level and on glass plates at ground level, after aerial application of an emulsion formulation of fenitrothion at the rate of 0.21 kg AI in 1.46 L per ha over a 16 ha plot in a plantation forest. Fenitrothion deposits were quantified by gas‐liquid chromatography. A wide variation was observed in deposits on foliage and at the forest floor. Deposits were relatively higher on foliar samples collected from the upwind side of a tree canopy than those on the downwind side. Similarly, the glass plate placed under a tree on the upwind side received relatively higher deposit than the one on the downwind side. However, the glass plates placed in the adjacent forest openings collected markedly higher deposits. Results clearly indicate filtration of the spray droplets by canopy foliage. Assessment of the average deposit of fenitrothion at ground level (mean deposit from all sampling locations) indicated that ca. 19.4% of the applied material reached the forest floor. Within a sampling station, correlation was poor between foliar depsits and those on glass plates under the same trees or in nearby clearings. Analysis of fenitrothion deposits on foliage collected at 1 and 2 h after application indicated that the droplets took, more than 1 h for deposition on the tree canopy. On the other hand, deposition on the glass plates at ground level appeared to be practically complete within 1 h post‐treatment. This was attributed to the higher sedimentation velocities of the larger droplets which tend to travel faster to the floor level than the smaller droplets which float for a longer period near the tree canopy.