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101.
通过对老湾成矿带各期构造作用、区域变质作用、岩浆作用、矿化富集作用研究,将老湾成矿带成矿构造体系演化分为三个阶段:加里东-华力西期深层次韧性剪切作用,形成的NNW向构造控矿因素深远,起初始富集作用;从印支晚期(236~214 Ma)开始,在燕山期或期前(132.5Ma)为脆-韧性剪切-右行走滑体系,矿液再次充填控矿形成现在的富矿体;燕山末期后发生了浅层次脆、韧性构造和构造推覆。并建立了老湾金矿带"早期老湾韧性剪切成矿构造系统"与"中期高角度右型走滑脆韧性断裂构造系统叠加"和"晚期构造掩盖或破坏"三期成矿构造演化体系。三期成矿构造演化体系的建立和"晚期老湾岩体推覆于龟山岩组上"的认识,极大地拓展了赋矿地层空间,为取得找矿突破提供重要理论依据。  相似文献   
102.
载金黄铁矿显微构造变形与金富集关系可以从显微-超显微尺度揭示金成矿作用和地质过程,探讨金的再活化或再聚集作用。在胶东焦家金矿带成矿期识别出4种类型的黄铁矿,文章应用光学显微镜、扫描电镜(SEM)、透射电镜(TEM)、电子背散射衍射(EBSD)和电子探针(EMPA)等技术方法,探讨黄铁矿显微构造特征、超微观结构与金的富集关系。结果显示:载金黄铁矿均不发育环带,其中w(Fe)为45.70%~46.85%,w(S)为52.57%~53.37%;显微构造变形既有脆性变形又有塑性变形;黄铁矿晶体优选方位(CPO)主要表现为平行于晶轴极密和复杂极密;黄铁矿晶格间距为0.58 nm,主要发育刃位错。焦家金矿带在金成矿作用过程中,可见金集合体经历了从复杂的纳米尺度到宏观尺度矿物载体富集的过程,包括成矿流体中金络合物、金-铋-硫族化合物富集等化学结构变化过程和纳米金、载金黄铁矿纳米颗粒、岩矿石显微-超显微构造微环境变化过程。因此,不同类型载金黄铁矿CPO受到化学结构变化和显微-超显微变形微环境变化的联合制约,间接反映出载金黄铁矿中金的富集与黄铁矿内部变形、表面形貌和结构缺陷有密切关系。  相似文献   
103.
为了解元素(尤其是重金属元素)在不同粒径大气颗粒物中的分布规律、污染特征及来源,于2016年在石家庄市采集PM1、PM2.5和PM10样品。利用等离子体质谱仪(ICP-MS)测定了Al、Ti、V、Cr、Mn、Fe、Cu、Zn、As、Sb、Hg、Pb和Cd共13种元素的质量浓度,采用富集因子(EF)法分析各种元素在PM1、PM2.5和PM10中的分布特征,并通过主成分分析法讨论了这些元素的主要来源。富集因子分析显示出Al、Fe、Ti、Mn受人为因素影响较少(EF<10),其他元素则出现显著至极强的人为影响,尤其是Cd元素(EF>103),并发现颗粒物粒径较小时,富集因子较大,即人为因素影响更重。主成分分析表明:PM1中元素有工业冶炼及燃煤活动、机动车燃油排放、生活燃煤3个来源,PM2.5中元素有地壳源、电厂及居民生活燃煤、金属冶炼等工业活动、机动车尾气4个来源,PM10中元素有化石燃料燃烧和地壳源、与机动车相关的道路扬尘及工业尘、垃圾焚烧及机动车排放与磨损、燃煤活动4个来源。  相似文献   
104.
川西高原草原地区的金矿成矿元素的表生地球化学特征   总被引:1,自引:1,他引:0  
赵琦 《物探与化探》1999,23(5):381-387,396
通过对川西高原草原地区的东北寨、马脑壳和哲波山金矿区的研究,总结该区的特殊的弱酸性偏还原的表生地球化学特征.并研究不同组元素的贫化和富集,不同粒级、不同深度的元素变化规律,提出金砷锑汞钨等元素是该区金矿的主成矿元素,总结出该区的表生地球化学特征.  相似文献   
105.
铅硐山铅锌矿床氧化带较发育,提出用氧化率来标定矿石的氧化作用特征。从矿区的气候、地形、构造、矿体产状、矿物组成和矿化主岩等对氧化富集作用的影响,总结了铅硐山矿床矿石氧化富集规律。并运用矿石氧化富集规律指导氧化矿开采,取得了较好的经济效益。  相似文献   
106.
Secondary copper enrichment in tailings at the Laver mine, northern Sweden   总被引:3,自引:2,他引:1  
 Field and laboratory studies of the sulphide-bearing tailings at Laver, northern Sweden, show that the present release of metals from the tailings is low, especially with regard to Cu. A large part of the Cu released by sulphide oxidation is enriched in a distinct zone just below the oxidation front. The enrichment zone occurs almost all over the tailings area except in areas with a shallow groundwater table. The Cu enrichment is caused by formation of covellite and adsorption onto mineral surfaces. The transport of Zn, Co, Cd, Ni and S seems to be controlled mainly by adsorption. No secondary zone or secondary minerals containing these metals have been found. Just below the groundwater table, metals are released into solution when the enrichment zone reaches the groundwater due to the low pH. An increased release of metals, especially Cu, can be expected in the future, since the enrichment zone is moving towards the groundwater table. Received: 4 December 1997 · Accepted: 17 December 1998  相似文献   
107.
粉煤灰土壤及所产蔬菜的有害元素含量变化和环境意义   总被引:1,自引:0,他引:1  
利用南京第二热电厂湿排的粉煤灰,进行了改良蔬菜土壤的试验,并对试验用的粉煤灰、不同施灰量的土壤及所产蔬菜共38 个样品的有害元素和放射性元素含量进行了系统的测定。结果表明:这些元素在土壤中的含量与粉煤灰施用量无明显相关性;在本次试验范围内施用粉煤灰没有造成土壤的污染;其所产蔬菜的这些元素含量也均低于国家卫生标准限值,食用是安全的。  相似文献   
108.
Dimethylsulfide enrichment in the surface microlayer of the South China Sea   总被引:5,自引:0,他引:5  
A total of 22 sea surface microlayer samples collected from the Nansha Islands waters of the South China Sea were analyzed for dimethylsulfide (DMS), chlorophyll a and nutrients including nitrate, phosphate and silicate. The DMS concentrations in surface microlayer samples ranged from 82 to 280 ng S/l with a mean of 145 ng S/l. A significant correlation was found between DMS and chlorophyll a data both in the surface microlayer as well as in the subsurface water. However, no correlation was observed between DMS and nutrient concentrations in the surface microlayer. The DMS concentrations were higher in all surface microlayer samples, compared with subsurface samples. The enrichment factor (EF) of DMS in the surface microlayer varied from 1.21 to 3.08 with an average of 1.95. The EF of DMS was significantly correlated with that of chlorophyll a in the microlayer. The enrichment of DMS in the microlayer may be due to two factors, including the in situ production from phytoplankton and the transportation from the underlying seawater. The diel variations in DMS and chlorophyll a concentrations were studied at a fixed station. The highest concentrations of DMS in the surface microlayer and subsurface water were simultaneously observed in the late afternoon (1800 h), while the highest levels of chlorophyll a were simultaneously found at night (0200 h).  相似文献   
109.
There are abundant coal and coalbed methane(CBM)resources in the Xishanyao Formation in the western region of the southern Junggar Basin,and the prospects for CBM exploration and development are promising.To promote the exploration and development of the CBM resources of the Xishanyao Formation in this area,we studied previous coalfield survey data and CBM geological exploration data.Then,we analyzed the relationships between the gas content and methane concentration vs.coal seam thickness,burial depth,coal reservoir physical characteristics,hydrogeological conditions,and roof and floor lithology.In addition,we briefly discuss the main factors influencing CBM accumulation.First,we found that the coal strata of the Xishanyao Formation in the study area are relatively simple in structure,and the coal seam has a large thickness and burial depth,as well as moderately good roof and floor conditions.The hydrogeological conditions and coal reservoir physical characteristics are also conducive to the enrichment and a high yield of CBM.We believe that the preservation of CBM resources in the study area is mainly controlled by the structure,burial depth,and hydrogeological conditions.Furthermore,on the basis of the above results,the coal seam of the Xishanyao Formation in the synclinal shaft and buried at depths of 700-1000 m should be the first considered for development.  相似文献   
110.
The aim of this study is to evaluate the feasibility of sludge digester effluent as feeding solution to enrich anaerobic ammonium oxidation (anammox) bacteria. The performance of the two parallel pilot scale‐upflow packed bed anammox reactors (UPBAn1 and UPBAn2) are examined in terms of the enrichment of anammox bacteria. The control experiment is set up conducting synthetic wastewater as feeding solution in the UPBAn1 reactor whereas, the sludge digester effluent is fed to the nitritation reactor and then the partially nitrated digester effluent to the UPBAn2 reactor. Anammox activities are evaluated by mass balances based on ammonium (NH4+), nitrite (NO2?), and nitrate (NO3?) analysis and NRR. Microbial community of anammox bacteria is analyzed using real‐time polymerase chain reaction (PCR). The results demonstrate that UPBAn 1 and UPBAn2 reactors are successfully enriched on days 64 and 40 with NRRs of 19.54 and 19.43 g N m?3 per day, respectively. This study reveals that both synthetic wastewater and digester effluent are suitable for the enrichment of anammox bacteria; however, digester effluent as feeding solution for enrichment of anammox bacteria based on the ease of process control and process stability is more advisable.  相似文献   
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