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淄博洪山—寨里煤矿地下水串层污染治理区水化学和硫同位素特征
引用本文:刁海忠,于 桑,李洪亮,等. 淄博洪山—寨里煤矿地下水串层污染治理区水化学和硫同位素特征[J]. 中国岩溶,2023,42(1):171-181 doi: 10.11932/karst20230113
作者姓名:刁海忠  于桑  李洪亮  尹秀贞  周建伟  刘红  王元新
作者单位:1.中化地质矿山总局山东地质勘查院, 山东 济南 250013;;2.山东省鲁南地质工程勘察院(山东省地质矿产勘查开发局第二地质大队), 山东 济宁 272100;;3.山东省地质矿产勘查开发局岩溶地质重点实验室,山东 济宁 272100;;4.中国地质大学(武汉)环境学院, 湖北 武汉 430074
基金项目:山东省鲁南地质工程勘察院(山东省地质矿产勘查开发局第二地质大队)开放基金课题(LNY2020-N13)
摘    要:在明确淄博洪山—寨里煤矿地下水串层污染治理区内水文地质状况、地下水流场特征等基础上,通过对矿井水、采空区水、矿排水、奥灰水、雨水、地表水的取样分析,掌握治理区的地下水水化学、硫同位素特征。选择接受大气降雨补给的区域、煤矿水聚集区、奥灰水聚集区以及奥灰水与煤矿水交叉混合区,分区对地下水水质现状及煤矿水和奥灰水之间水力联系情况进行分析判断。通过对比分析治理前后研究区水质情况,发现治理后奥灰水仍呈现高${rm{SO}}_4^{2-}$浓度、高硬度、高TDS特征,且硫酸盐主要来源于煤矿水,治理后洪山、寨里煤矿地下水串层通道依然存在,串层污染情况持续进行,且污染较治理前有加重趋势。则今后治理工作应进一步查清、控制导水通道,控制矿坑水水位,避免其污染奥灰水。

关 键 词:废弃煤矿   水化学特征   硫酸盐硫同位素   串层污染
收稿时间:2022-01-20

Analysis on the hydrochemical and sulfur isotope characteristics of the groundwater in cross-strata pollution control area of Hongshan and Zhaili coal mines in Zibo
DIAO Haizhong, YU Sang, LI Hongliang, YIN Xiuzhen, ZHOU Jianwei, LIU Hong, WANG Yuanxin. Analysis on the hydrochemical and sulfur isotope characteristics of the groundwater in cross-strata pollution control area of Hongshan and Zhaili coal mines in Zibo[J]. CARSOLOGICA SINICA, 2023, 42(1): 171-181. doi: 10.11932/karst20230113
Authors:DIAO Haizhong  YU Sang  LI Hongliang  YIN Xiuzhen  ZHOU Jianwei  LIU Hong  WANG Yuanxin
Affiliation:1. Shandong Geological Prospecting Institute, China Chemical Geology and Mine Bureau, Jinan, Shandong 250013, China;;2. Shandong Provincial Lunan Geology and Exploration Institute (Shandong Provincial Bureau of Geology and Mineral Resources No.2 Geological Brigade), Jining, Shandong 272100, China;;3. Key Laboratory of Karst Geology , Shandong Provincial Bureau of Geology and Mineral Resources, Jining, Shandong 272100, China;;4. School of Environmental Studies, China University of Geosciences, Wuhan, Hubei 430074, China
Abstract:Since the closure of Hongshan and Zhaili coal mines in Zibo City, Shandong Province, the pumping and drainage of groundwater has stopped, leading to the rise of water level in coal mines. Consequently, Ordovician limestone water was polluted to different degrees through the hydraulic connection channels such as broken well pipes. The main pollution factors, like ${rm{SO}}_4^{2-}$ , TDS, total hardness, etc., resulted in the deterioration of karst water below the drinking standard in the study area, and hence seriously affected local residents’ living and economic activities. The main water-bearing strata in the study area include loose rock pore aquifers, clastic rock fissure aquifers or interlayer karst fissure aquifers and carbonate rock karst aquifers. As the main coal measure aquifer in the study area, the fissure aquifer is the direct water source of coal mining. In the natural state, there lacks hydraulic connection between the fissure aquifer and the underlying Ordovician karst aquifer. But because the impermeable layer was damaged by coal mining, the water channel has been formed. During the mining process, the fissure water in the coal measure strata was basically drained, and the Ordovician limestone water entered the pit by the way of jacking recharge. After the coal mine was closed, the level of the coal mine water rose, and the Ordovician limestone water was replenished through the connecting place.In order to provide a scientific basis for future remediation of groundwater pollution in Hongshan and Zhaili coal mine areas and other similar mining areas, this study was carried out on the hydrochemical and isotope characteristics of the water after treatment in the study area, and a qualitative and quantitative analysis was conducted on the quality characteristics and treatment effects of the groundwater. To conduct the hydrochemical and isotope analyses based on hydrogeological conditions, characteristics of groundwater flowing field and sampling points before treatment, a series of monitoring points were set up along the groundwater flowing direction from the upstream of the pollution source area. Sampling types include coal mine water, Ordovician limestone water, rain water, surface water, etc. Coal mine water includes mine water, goaf water and mine drainage.Through the sampling test, the results of hydrochemical and isotope analyses show that there is a hydraulic relation and mutual influence between Ordovician limestone water and coal mine water in the study area. The sulfate in groundwater in this area mainly comes from the oxidation of sulfide minerals in coal-bearing strata, and the Ordovician limestone water is polluted by the coal mine water in cross-strata, which leads to the increase of sulfate concentration in Ordovician limestone water.Results show that the hydrochemical type of Ordovician limestone water is complex, and some Ordovician limestone water is characterized by high ${rm{SO}}_4^{2-}$ concentration, high hardness and high TDS. The concentration range of high ${rm{SO}}_4^{2-}$ is basically consistent with the coal mine area and its downstream. The normal Ordovician limestone water environment in the area has been disturbed, because of the mixture of extraneous water. The hydrogen and oxygen isotopic compositions of some Ordovician limestone water and coal mine water are similar, and δS values present positive and negative deviations. According to the characteristics of sulfates and sulfur isotopes, the sulfates in Ordovician limestone water mainly come from the cross-strata pollution of coal mine water, and the pollution is more serious than it is before treatment. It is speculated that there is still a hydraulic connection between coal mine water and Ordovician limestone water. Therefore, further treatment is suggested to identify and control the water channel, strengthen the pumping and drainage of coal mine water and encourage the comprehensive utilization. Besides, the water level of mine pit should be controlled to avoid the pollution of Ordovician limestone water.
Keywords:abandoned coal mine  hydrochemical characteristics  34<  sup>S isotope  cross-strata pollution
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