从电法勘探资料分析宋楼煤矿主斜井突水因素     

时晗 《物探与化探》2005,29(2):135-137

根据宋楼煤矿主斜井直流电法勘探资料及矿井地质及水文地质条件的分析,煤矿主斜井突水原因应该是来自第四系砂砾石含水层及深层地下岩溶水。通过电法勘探确定裂隙发育带、富水区域、涌水部位,对此处实施钻孔注浆堵水后,恢复生产。  相似文献   

煤矿水害多源信息预测方法研究   总被引：1，自引：0，他引：1  

崔三元  崔若飞 《物探与化探》2005,29(6):557-560,564

基于MAPGIS平台,用Visual C＋＋对其进行二次开发,研制了煤矿水害多源信息预测系统.通过对地震、电法、水文地质等多源数据进行处理后,在MAPGIS系统下进行成图、配准和空间定量分析,建立了预测模型.用该系统对煤矿实际资料进行了处理,结果表明其预测结果较传统方法更为准确.  相似文献   

矿业开发与环境保护关系综述   总被引：4，自引：0，他引：4  

郭路  李云峰  姬亚东 《西北地质》2005,38(2):94-98

笔者介绍了我国矿业发展经历的3个阶段，归纳出我国矿业开发带来的矿山环境问题主要有：地面塌陷、占压破坏土地、改变地质构造、破坏水资源、污染水、污染土壤、污染大气、瓦斯爆炸及河床抬高等。分析了环境恶化的原因主要与区域地质环境条件、历史、经济技术、矿山企业和地方保护主义等因素有关。最后提出了防治矿山环境恶化的对策，对难以治理的地区以预防、避让为主，历史问题由政府和企业共同解决，落实“谁开发、谁保护；谁受益、谁治理；谁破坏、谁恢复”的生态环境保护新机制，加强监管，加强防治对策研究，走综合勘探、综合评价、综合开发、综合利用的发展道路。  相似文献   

永城煤矿区矿井经济环境价值综合评价     

刘金平张幼蒂  王明明 《中国煤田地质》2005,17(2):40-42

在初步估算永城煤矿区的环境成本的基础上，对该矿区某矿井经济环境综合价值进行了评价和分析。当考虑矿区煤炭环境成本时，煤炭资源开采的净现值变小，该矿井煤炭资源开采的经济环境综合价值变小。进一步计算了不同环境成本和贴现率时的净现值，为动态决策服务。  相似文献   

淄博市洪山、寨里煤矿地下水串层污染形成原因及防治     

吕华刘洪量  马振民徐品 《中国煤田地质》2005,17(4):24-27,31

淄博市洪山、寨里煤矿区隐伏的奥陶系灰岩裂隙岩溶水污染严重。水质污染突发于矿坑全面闭坑以后，污染范围与矿坑水区一致，地下水污染组份与矿坑水的高含量组份相同。水质恶化主要由矿坑水串层污染所致。在此针对串层污染形成原因及影响因素，提出了防治对策。  相似文献   

内陆盆地的盐分布与平衡分析研究   总被引：9，自引：0，他引：9       下载免费PDF全文

董新光  姜卉芳  邓铭江  周金龙 《水科学进展》2005,16(5):638-642

在总结已有研究成果和系统分析水文、土壤、灌溉、水盐监测资料的基础上,应用系统分析方法、水盐运移理论和水盐平衡原理,通过对盆地、流域、灌区、农田和土壤剖面等不同层次盐分分布与盐平衡分析计算,分析了内陆盆地不同层次的“干排盐”形成与特征,认为干排盐是必不可少的,必须系统地考虑不同层次干排盐出路与动力条件,才能有效地治理灌区盐渍化问题。  相似文献   

云南矿业支柱产业建设的重点、难点及对策研究   总被引：4，自引：0，他引：4  

林幼斌  赵磊 《矿物岩石地球化学通报》2002,21(2):98-102

云南矿业发展现状尤其是磷化工和有色金属等优势资源的调研和分析结果表明，矿业已成为云南工业的主体产业群体，影响云南矿业发展的难点主要是企业规模偏小，产品结构不合理，企业整体经济效益下降，国有企业困难面大，地质勘探投入少，矿山建设落后等，并据此讨论了矿业作为云南省支柱产业发展的思路和重点，提出相应的对策和建议。  相似文献   

高峰公司100号矿体矿床建模与矿山生产动态管理的研究     

邓金灿 《矿产与地质》2002,16(5):306-312

重点论述高峰锡矿 10 0号矿体的矿床数学经济模型的建立 ,分析模型在采矿、选矿等矿山生产动态管理中的作用及意义  相似文献   

Experimental Study on Mine Spoils During Superficial Geochemistry Processes     

王一先  白正华 《中国地球化学学报》2002,21(4)

Based on the mineral and chemical compositions of spoils taken from the Shilu Cu-Mo deposit and Hetai gold deposit, the leaching and batch experiments were made on spoils taken from these two deposits using the leaching column designed by the authors. The experimental results showed that it is not always true that the mine drainage is acidic. Its acidity depends on acid-buffering capacity of gangue, host rock and its alteration mineral assemblage. The composition of the drainage water is related with the interaction between superficial or underground water and solid materials in the spoils, including minerals, hydroxides and amorphous substances. The leaching extent of the element is related with its occurrence form in the deposit. The preferential flow results in leaching-out of heavy metals in large amounts. So it is important to prevent the generating of preferential flow in the system. The results will provide very important grounds for the comprehensive management of land and ecological rehabilitation of the mine site.  相似文献   

Evapotranspiration from citrus trees growing in sandy soilunder drip irrigation with saline water     

杨胜利  Tomohisa Yano 《中国科学D辑(英文版)》2002,45(Z1)

An experiment on evapotranspiration from citrus trees under irrigation with saline waterwas carried out for 4 months. Two lysimeters planted with a citrus tree in the green house wereused. One lysimeter was irrigated with saline water (NaCl and CaCl2 of 2000 mg/L equivalence,EC = 3.8 dS/m, SAR = 5.9) and the other was irrigated with freshwater using drip irrigation. Theapplied irrigation water was 1.2 times that of the evapotranspiration on the previous day.Evapotranspiration was calculated as the change in lysimeter weight recorded every 30 minutes.The lysimeters were filled with soil with 95.8% sand. The results of the experiment were as follows.(i) The evapotranspiration from citrus tree was reduced after irrigation with saline water. Theevapotranspiration returns to normal after leaching. However it takes months to exhaust the saltfrom the tree. ( ii ) To estimate the impact of irrigation with saline water on the evapotranspirationfrom citrus trees, the reduction coefficient due to salt stress (Ks) was used in this experiment.Evapotranspiration under irrigation with saline water (ETs) can be calculated from evapotranspira-tion under irrigation with freshwater (ET) by the equation ETs = Ks× ET. Ks can be expressed as afunction of ECsw. (iii) The critical soil-water electrical conductivity (ECsw) is 9.5 dS/m, beyondwhich adverse effects on evapotranspiration begin to appear. If ECsw can be controlled at below9.5 dS/m, saline water can be safely used for irrigation.  相似文献