高级检索

    内蒙古东乌珠穆沁旗查干敖包铁锌矿矿山地质环境遥感监测与评价

    Remote sensing-based monitoring and assessment of the geological environment of the Chagan'aobao iron-zinc mine in East Ujimqin Banner, Inner Mongolia

    • 摘要: 开展单一矿山长时序遥感监测和矿山地质环境评估,分析矿区土地损毁与生态修复的变化过程,是开展井工开采矿山生态修复工程设计、实现“一矿一策”的重要基础工作。该文以内蒙古查干敖包铁锌矿为研究区,采用2008—2024年共17期遥感数据进行监测,并综合岩性组合、边坡结构等13个因子,构建单一矿山矿区地质环境遥感评价模型,识别矿山地质环境影响程度。结果表明:2008年,查干敖包铁锌矿的采矿损毁土地面积为59.47 hm2, 至2024年增加到158.29 hm2,且在2022年达到峰值165.21 hm2;适当控制塌陷坑的塌陷规模,并及时开展生态修复,可有效遏制矿区采矿损毁土地面积的增长;区域矿山地质环境一般影响区、较严重影响区和严重影响区的面积分别为32.34 hm2,132.37 hm2和7.15 hm2。建议对塌陷坑等严重影响区进行削坡卸载、坑底压脚等工程处理,降低地灾风险,土壤重构、植被恢复等宜暂缓开展,对尾矿库、采矿工业场地等较严重影响区宜开展区域沉降影响监测,加强日常巡查,对一般影响区可部署开展覆土、植草等生态修复。

       

      Abstract: Remote sensing-based, long time-series monitoring and geological environment assessment of individual mines enable the analysis of variations in their land damage and ecological restoration. These efforts are fundamental for the engineering design of ecological restoration in underground mines and for achieving mine-specific solutions. This study investigated the Chagan'aobao iron-zinc mine in East Ujimqin Banner, Inner Mongolia. The 17-phase remote sensing data reveal that mining activities in the mine damaged 59.47 hm2 of land by 2008, which expanded to 158.29 hm2 by 2024, with the damaged land area peaking at 165.21 hm2 in 2022. Appropriate control of the scale of collapse pits and prompt ecological restoration can effectively curb the expansion of land areas damaged by mining. By integrating 13 factors, including lithologic associations and slope structures, a remote sensing-based assessment model for the geological environments of a single mine was constructed, allowing for the effective identification of the degree of impacts on a mine's geological environment. Within the region, the areas classified as general, moderate, and severe mining-affected zones covered areas of 32.34 hm2, 132.37 hm2, and 7.15 hm2, respectively. For severe mining-affected zones like collapse pits, it is recommended to implement engineering measures, including both slope cutting for unloading and footing placement at pit bottoms, to mitigate geological hazard risks. Meanwhile, soil reconstitution and vegetation restoration should be temporarily deferred. For moderate mining-affected zones, including tailings ponds and mining industrial sites, it is necessary to monitor regional subsidence impacts and enhance routine inspections. Additionally, ecological restoration measures, such as soil covering and grass planting, can be deployed for general mining-affected zones.

       

    /

    返回文章
    返回