2016—2024年淮南矿区采煤沉陷积水区范围变化及水色变化

    Changes in the scope and water color of coal mining subsidence waterlogging area in Huainan Mining Area from 2016 to 2024

    • 摘要: 在东部高潜水位矿区,煤炭资源的过度开发导致大范围地表沉陷和积水,沉陷区相互连接并形成了大片水域。因此,准确掌握地表沉陷积水及其水环境信息对于采煤沉陷积水区治理至关重要。本文选取了2016—2024年所有可用的Landsat-8 SR影像,绘制了采煤沉陷积水区范围,并对6—9月的影像进行平均值合成,计算了水色指数。研究结果显示:淮南矿区采煤沉陷积水区面积在2016—2024年间波动显著,整体呈现“增长-下降-增长”的趋势,其中,2018—2020年的表观面积下降主要受水上光伏铺设影响。具体而言,2016年积水区总面积为64.76 km2,占矿区总面积的11.99%。其中,季节性积水占30.39%。随后几年,水域面积经历了波动变化,最终在2024年增至82.46 km2;此时积水结构发生根本性逆转,季节性积水区面积激增至52.02 km2(占比达63.09%),取代常年积水成为主体,且表现出极高的空间不稳定性。此外,淮南矿区季节性积水区的水色状况整体良好,多处于FUI 6~9级范围,优于常年积水区。2016—2024年,季节性积水区中优良水色(FUI 6~9级)的面积大幅增加,由12.17 km2增至24.69 km2;而常年积水区水色处于FUI 10~13级的面积占比则长期维持在较高水平。这表明淮南矿区采煤沉陷积水区的水色情况整体趋势向好,但常年积水区仍需重点关注。就积水程度而言,季节性积水区的水色指数等级总体低于常年积水区。在淮南矿区中,朱集东矿井的水色相对较好,而顾桥矿和丁集矿则相对较差,但从整体趋势来看,各矿井的水质状况均在逐步改善。

       

      Abstract: In eastern mining regions with high groundwater level, the overexploitation of coal resources leads to extensive surface subsidence and waterlogging, where subsidence areas interconnect to form vast water bodies. Therefore, accurately capturing information on surface subsidence waterlogging and its aquatic environment is crucial for the governance of coal mining subsidence waterlogging areas. This study selects all available Landsat-8 SR images from 2016 to 2024 to map the extent of subsidence waterlogging areas and synthesizes mean value images from June to September to calculate the Forel-Ule Index (FUI). The results indicate that the coal mining subsidence waterlogging area in Huainan Mining Area fluctuates significantly between 2016 and 2024, presenting an overall “increase-decrease-increase” trend; notably, the apparent decrease in area from 2018 to 2020 is primarily influenced by the installation of floating photovoltaic panels. Specifically, in 2016, the total waterlogging area is 64.76 km2, accounting for 11.99% of the total mining area, with seasonal waterlogging area constituting 30.39%. In subsequent years, the water area experiences fluctuations, ultimately increasing to 82.46 km2 in 2024. At this point, the waterlogging structure undergoes a fundamental reversal: the seasonal waterlogging area surges to 52.02 km2 (accounting for 63.09%), replacing perennial waterlogging as the dominant type and exhibiting high spatial instability. Furthermore, the water color condition in seasonal waterlogging areas is generally good, mostly ranging between 6 and 9 of FUI, which is superior to that of perennial waterlogging areas. From 2016 to 2024, the area of excellent water color (FUI 6-9) within seasonal waterlogging areas increase significantly from 12.17 km2 to 24.69 km2, while the area of FUI 10-13 in perennial waterlogging areas remains at a high level for an extended period. This indicates an overall improving trend in the water color of subsidence waterlogging areas in Huainan Mining Area, although perennial waterlogging areas still require focused attention. In terms of waterlogging, the FUI levels of seasonal waterlogging areas are generally lower than those of perennial waterlogging areas. Among the mines in the Huainan Mining Area, the water color in Zhujidong Mine is relatively better, whereas that in the Guqiao and Dingji mines is relatively poorer; however, the overall trend shows that water quality conditions in all mines are gradually improving.

       

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