Abstract

Highlights

  • The enrichment mechanism of high-fluoride mine water was controlled by geologic processes and coal mine activity.
  • Hydrochemical evolution including mineral dissolution, desorption and cation exchange causes the release of F trapped in strata into groundwater.
  • Mudstone and siltstone from aquiclude have a high F concentration and water-rock interactions in goaf accelerate F-accumulation in mine water.
  • The conceptual model of high-fluoride mine formation was first established: high-F mine water was controlled by geologic processes and coal mining.

Excessive fluoride ion (F) concentrations in mine water affected by the geologic processes and coal mine activity prevent the reusage of it as domestic and production water resources. There are few researches on the accumulation mechanism of fluoride in mine water. In this study, 71 water samples and 39 rock samples were collected from 9 mines of the Inner Shaanxi-Mongolia Contiguous area for chemical analyses and laboratory experiments. Results indicate that the concentration of F in mine water increased with the gradual increase of the coal mining depth. The average concentration of F in no.3-1 coal mine water is higher than that in no.2-2 coal mine water. And concentrations of F exceed the China national standard for drinking water quality (upper limit of 1 mg/L), which is closely related to fluoride in the no.3-1 coal roof groundwater and water-rock interaction in the goaf. The main hydrogeochemical processes include mineral dissolution (fluorapatite and hornblende), desorption of exchangeable F from clay minerals (mica, illite, kaolinite and chlorite) and cation exchange between Ca2+ and Na+. Furthermore, long-term further water–rock interactions result in F accumulation in mine water. Alkaline environments, decreased particle size of rock, and increased temperature all favor release of F from clay mineral surface into mine water. Finally, conceptual model of high-fluoride mine water was first proposed, and the formation of high-fluoride mine water can be summed as two stages including water-rock interaction in groundwater and secondary water-rock interaction in goaf. This study helps to improve our understanding of genesis of high-fluoride mine water and our capability of predicting the future concentration, which may provide foundation for manage and utilization of mine water.

Introduction

Fluoride is a micronutrient essential for the human body. And moderate fluoride intake is beneficial in the prevention of dental caries or tooth decay. However, excessive intake of F for a long time can cause dental or skeletal fluorosis, or even worse, genetic damage, mental retardation or cancer (Ayoob and Gupta, 2006; Yadav et al., 2017; Hossain and Patra, 2020). Abundant in Earth’s crust (625 mg/kg), the element fluorine forms fluoride exists extensively in soil, rocks, and aquifer sediments (Amini et al., 2008). This will lead to fluoride accumulation in fresh groundwater, ultimately.

The main way of human exposure to F is through drinking water especially groundwater (Rashid, et al., 2020). It is estimated that more than 200 million people in 28 countries worldwide (Shah and Danishwar, 2003; Rafique et al., 2009; Souza et al., 2013; Shakir, et al., 2016; Carl et al., 2020; Podgorski and Berg, 2022) depend on groundwater with fluoride concentrations that exceed the national WHO standards of 1.5 mg/L (WHO, 2004). In China, geological high fluoride concentration groundwater is mainly distributed in arid and semi-arid northwestern regions. Approximately 20 million people are negatively impacted by chronic endemic fluorosis in China (Jia et al., 2018; Wang et al., 2020). Hence, the Chinese government has set allowable limit for fluoride in drinking water/groundwater as 1.0 mg/L (Ministry of Health of China, 2010). Meanwhile large coal mines are mainly located in the northwest, and mine water almost comes from groundwater, consequently, high-F-high-fluoride is abbreviated to high-F- mine water is widely distributed in Northwest China (Wang, et al., 2022).

Over the past decades, many scholars have studied on sources, distribution and formation of high-F groundwater (Chae et al., 2007; Guo et al., 2007; Meenakshi et al., 2004; Rashid et al., 2020). Dissolution of fluorine-rich rocks and minerals is an important geogenic source of F enrichment in water. Fluorine-bearing rocks are often associated with granites, alkali granites, and hydrothermal deposits (Wang et al., 2021). And Fluoride has been found to be rich in fluorite (CaF2), topaz (Al2(SiO4)F2), micas [AB2–3 (X, Si)4O10(O, F, OH)2], fluorapatite (Ca5(PO4)3F)- Chae et al., 2007; Jadhav et al., 2015. Usually, F is increasingly released and accumulated in the groundwater via water–rock interactions (Shah and Danishwar, 2003). The enrichment of fluoride in groundwater in Sri Lanka is mainly due to the dissolution of hornblende and mica in black gneiss (Young et al., 2011). Controlled by climate conditions, fluorine-rich rock types and anthropogenic activities, the accumulation of fluoride in groundwater exhibits a zonality and significant differences. Horizontally, the concentration of fluoride gradually increases along the groundwater flow path from the recharge area, through the runoff area, to the discharge area (Alarcon-Herrera et al., 2013). Vertically, affected by evaporation, fluoride concentration in shallow groundwater gradually declines with increasing depth (Yadav et al., 2019). Besides, other processes that lead to high-F groundwater include Na–Ca cation exchanges, competitive adsorption and alkaline environment (Schafer, 2020). The exchange is an important hydrogeochemical process in the enrichment of fluorine in groundwater in the Ordos Basin (Su, et al., 2021). Furthermore, under alkalescency and alkaline (high pH) conditions, OH and HCO3 can mobilize F from fluorine-bearing minerals such as clay minerals and Fe/Al oxyhydroxides into groundwater (Alcaine, et al., 2020).

Although the enrichment mechanism of fluorine in groundwater has been studied, no studies have evaluated the formation mechanism of fluorine in mine water controlled by the geologic processes and coal mine activity. In recent years, with the increasing development of coal mining, high-F mine water is more widespread than before in many areas, especially in areas with semi-arid climates, such as Northwest China (Wang, et al., 2022). During coal mining, groundwater gushes into the coal face, goaf, and becomes mine water (Qu, et al., 2020). Thus, high-F mine water is controlled by geologic processes and anthropogenic mining activities. Coal mining changes the original input, output, and groundwater runoff of hydrological systems, thereby causing stronger hydraulic connections between the related aquifers and a stronger water-rock interaction (Zhang, et al., 2022). Besides, goafs are formed after coal mining. In goaf, further water-rock interaction occurs between broken rock and mine water, which promotes the release of fluorine into mine water again. Many physical and chemical reactions are involved in the water–rock interaction process, and it affects both mine water quality and coal or rock masses (Zhang, et al., 2021, 2023). Few researches has focused on release of fluorine in goaf. In conclusion, under coal mining, the fundamental mechanism leading to high-F mine water and controlling factors on release of fluorine in goaf are still not fully understood.

The Inner Mongolia-Shaanxi contiguous area is characterized by an arid and semi-arid climate, with scarce rainfall, and a fragile ecosystem (Qu et al., 2022). The mine water guarantees the water resource supply for production, living and ecology of the local power plants, and chemical industry (Zheng et al., 2021). With the increasing mining depth, and the change of geological conditions, fluoride pollution of mine water is becoming increasingly prominent. This undoubtedly poses potential obstacles to mine water resources utilization. However, there are few research reports the geochemical processes that control F enrichment of mine water in the study area. This research aims to (1) characterize the hydrogeochemical properties of high-F mine water using Piper plots. (2) study the lithological features, mineral composition of F-containing rocks by the scanning electron microscope and energy disperse spectroscopy (SEM-EDS). (3) unravel the main water-rock interaction and controlling factors of high-F mine water by laboratory simulation experiment.

Section snippets

Location and climate

The Inner Mongolia-Shaanxi contiguous area lies in the upper reach of the Yellow River and at the border of Shaanxi and Inner Mongolia, Northwest China (Qu et al., 2022). The study area is located in the northern region of Ordos basin with an average elevation of approximately 1200 m. It belongs to a semi-arid continental climate characterized by frigid winters and scorching summers. The average annual precipitation is 310–500 mm and 60% of the rainfall is concentrated from July to September.

Water sampling and analysis

In this study, a total of 71 groundwater and mine water samples were collected from 9 minefields, from July 2018 to July 2022. The collected water samples comprised 49 mine water samples with 32 specifically associated with the 2-2 coal seam (collected in July 2018) and the remaining 17 samples tied to the no.3-1 coal seam (collected in July 2022). These mine water samples covered different parts of the mine including mining working face, the goaf, the main mining roadway, and the central water

Hydrochemistry

The hydrochemistry and fluoride concentration of the water samples are shown in Table 1. Waters of different types in the study area are characterized by a pH range of 7.55–10.87, classified as weakly alkaline to alkaline in nature. The pH values of surface water and the Quaternary phreatic groundwater were both less than 8, while the pH values of Zhiluo Formation and Yan’an Formation groundwater and mine water were all greater than 8.0. The average TDS of Quaternary and Zhiluo Formation

Formation of high-F groundwater

From the water general chemistry and rock geochemistry, it can be gotten that high-F mine water of 3-1 coal is closely related to high-F groundwater of no.3-1 coal roof. And, factors control the geochemistry formation process of no.3-1 coal roof high-F groundwater should be discussed in detail.

Conclusions

In the study area, high-F groundwater occurs mainly in no.3-1 coal roof aquifer (with an average of 4.32 mg/L), and high-F mine water occurs mainly in no.3-1 coal seam (with an average of 6.36 mg/L). And high-F mine water of no.3-1 coal is closely related to high-F groundwater from no.3-1 coal roof. No.3-1 coal roof groundwater fluorine is originated from the dissolution of fluoride-bearing minerals involving in fluorapatite, augite, and mica. Furthermore, the accumulation of fluoride in no.3-1

CRediT authorship contribution statement

Tiantian Wang: Writing – original draft, laboratory experiment, data analysis. Jian Yang: Writing – review & editing. Dewu Jin: Writing – review & editing. Guoqing Li: Writing – review & editing. Zhenfang Zhou: Data collection and, Formal analysis. Jiankun Xue: Water sampling and, Formal analysis. Hongbo Shang: Water sampling and, Formal analysis.

Declaration of competing interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgment

This research was financially supported by the National Natural Science Foundation of China (No.42307113), the Natural Science Foundation of Shaanxi province (2023-JC-QN-0291, 2022JQ-471) and National Key Research and Development Program of China (2023YFC3700067-2).

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