华北型煤田封闭采区地下水回升渗流特征与水质演化规律

Groundwater rebound and seepage characteristics and water quality evolution in a sealed mining area in North China type coalfield

  • 摘要:
    背景 煤矿采区封闭诱发的地下水回升过程所伴生的渗流场演变与水质演化,对矿井水害防控、水资源循环利用具有重要影响,系统揭示其渗流−水化学协同作用机制是推进矿区水系统协同治理与资源化开发的基础科学问题。
    方法 以山东枣庄滨湖煤矿116封闭采区为工程背景,采用水化学测试、数值模拟、理论计算方法,分析封闭采区内积水回升渗流特征以及离子浓度、矿相演化规律,对地下水回升及水化学演化模式进行表征。
    结果与讨论  (1)滨湖煤矿116采区现有积水主要分布于采区西侧,根据封闭前涌水量计算,积水回升灌满整个采区空间预计需要426 d。采区封闭后0~90 d内,突水点持续涌水,采空区水位快速回升至−450~−250 m,封闭后90~360 d内,采空区水位回升速度减缓,采空区两侧水位升至−150 m,之后水位变化不大,至封闭455 d时积水完全灌满采空区,与预计结果基本相符,此时地下水流场基本达到平衡状态。(2)奥灰水与十四灰水在沿裂隙上涌及突水过程中,阳离子交换加速,Na++K+浓度快速上升,Ca2+、Mg2+显著下降,此阶段钠长石、钾长石及岩盐等矿物相增多,石英、方解石及白云石因溶解或沉淀减少。(3)采空区封闭后,积水回灌过程中水−岩作用持续,但阳离子交换速率减缓,矿物相变化趋势与突水阶段相似但强度减弱,最终形成以高Na+/K+、低Ca2+/Mg2+为特征的水化学平衡体系,整个过程反映了从动态突水扰动到封闭采空区缓慢自平衡的封闭采区积水化学演化模式。研究结果为揭示相似背景下的采空区积水水环境演化规律提供了参考,为封闭矿井地下水资源开发利用提供了理论依据。

     

    Abstract:
    Background The seepage field and water quality evolution associated with the groundwater rebound induced by the sealing of mining areas significantly affects the prevention and control of mine water hazards, as well as the recycling of water resources. Systematically elucidating the mechanisms underlying the seepage-hydrochemistry synergy of groundwater is recognized as a fundamental scientific issue for promoting the collaborative management and resource development of the water systems in mining areas.
    Methods Based on the engineering background of the sealed No.116 mining area in the Binhu Coal Mine, Zaozhuang, Shandong Province, this study investigated the groundwater rebound and seepage characteristics, along with the associated evolutionary patterns of ion concentrations and mineral phases in groundwater, using hydrochemical tests, numerical simulation, and theoretical calculation. Furthermore, this study characterized groundwater rebound and hydrochemical evolutionary models.
    Results and Conclusions  The existing accumulated water was primarily distributed in the western part of the No.116 mining area in the Binhu Coal Mine. Based on the water inflow before the sealing of the mining area, it can be estimated that the accumulated water would fill the whole goaf within 426 days. Specifically, within the initial 90 days after sealing, the water inrush points continuously discharged water, causing the groundwater level in the goaf to rise to −450 to −250 m rapidly. Within 90‒360 days post-sealing, the groundwater rebound in the goaf slowed down, with the water level on both sides of the goaf reaching −150 m. Consequently, the water level remained relatively stable until at day 455 post-sealing, when the goaf was full of accumulated water. The process was largely consistent with the expected results. By this time, the groundwater flow field roughly reached equilibrium. During the water rebound along fractures and water inrush from Ordovician limestone and the fourteenth limestone aquifers, cation exchange was accelerated, with the Na+ and K+ concentrations increasing rapidly and the Ca2+ and Mg2+ concentrations decreasing significantly. At this stage, the quantities of mineral phases such as albite, potassium feldspar, and halite increased, while those of quartz, calcite, and dolomite decreased due to dissolution or precipitation. After the goaf sealing, water-rock interactions persisted during the reinjection of the accumulated water, but the cation exchange rate slowed down. The mineral phases showed similar but weakened variation trends compared to the water inrush stage. Finally, a hydrochemical equilibrium system characterized by high Na+/K+ and low Ca2+/Mg2+ concentrations was formed. The whole process reflects the hydrochemical evolution model of the sealed mining area from dynamic water inrush disturbance to slow self-equilibrium. The results of this study provide a reference for revealing the evolutionary pattern of the water environment in goaves under similar settings and offer a theoretical basis for the development and utilization of groundwater resources in sealed mines.

     

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