Statistical analysis of tailings ponds in China

https://doi.org/10.1016/j.gexplo.2020.106579Get rights and content

Highlights

  • 5189 tailings ponds in China have been discussed in this paper. Especially, average altitude of tailings ponds is 699.4 m, the occupied land is 1884.0 km2, and the strip between the tailings wastes and soil are accumulated to 14674.4 km.

  • The tailings ponds were widely distributed throughout the country, especially, highest horizontal distribution density occurs in north Hebei province, with a mean density of >0.02/per km2.

  • The horizontal and vertical distribution of tailings ponds in the watershed was discussed.

Abstract

While tailings wastes have attracted public concern in China, the knowledge of their numbers, distribution, land occupation, perimeter, and altitude is incomplete. Based on statistics and geographic information system (GIS) method, the present study investigated 5189 of tailings ponds (TPs) in order to understand the present situation of tailings in China. Overall, this study revealed that the occupied land of TPs is about 1884.0 km2, average altitude is 699.4 m, and the strip between the tailings wastes and soil accumulated to 14,674.4 km. This is harmful to the security of closed biomes community. Besides, TPs are widely scattered, especially, the distribute density which ranges from 0.009 to 0.05/km2 are located in the northern Hebei Province, Liaodong Peninsula, Shandong Peninsula and western Henan province. In terms of watershed for TPs, the ascending order is Huaihe River, Heilongjiang River, Pearl River, Liaohe River, Yellow River, Yangtze River, Haihe River; and the land usage is Huaihe River < Pearl River < Liaohe River < Heilongjiang River < Yangtze River < Haihe River < Yellow River. In a nutshell, tailings wastes should be considered a huge environmental threat in China.

Introduction

The tailings ponds (TPs) are the facilities to store mines wastes from mining operations. These mining wastes are the major contaminants in the world, and ranked 18th among the most important public hazards (Xie et al., 2009). In recent decades, mining activities have intensified in China and produced huge amounts of tailings wastes. Hence, it is a major concern for its heavy metal pollution (Liu et al., 2018; Wang et al., 2016; Yao et al., 2016), tailings ecological restoration (Dacal et al., 2019; Huang et al., 2011; Le et al., 2016), chemical weathering and tailings CO2 sequestration (Li et al., 2011; Tang, 2017; Van et al., 2015).

Nevertheless, existing studies are still inadequate in many ways. Firstly, there are insufficient reliable data that could reflect the fundamental feature of TPs in China, and the amounts of TPs in China are still uncertain (Table 1). Secondly, few studies examined the tailings wastes across the entire China, but merely reported regional issues in Jiaodong peninsula (Zhou et al., 2017), Qinlin orogenic belt (Qiang, 2013; Wang et al., 2017) in recent years. To this end, this paper intends to focus on the primary data (distribution, altitude, land occupation, perimeter) of TPs in China. The idea is to reveal their basic features, and ultimately attract attention from the public and government authorities in China.

Section snippets

Research method

The current study obtained the approximate location of TPs from government documents, published journal articles, online news, and internal information (Appendix 1). Then, we compared the field investigation of the TPs with remote sensing data (especially the basic size, location and topography). From 2013 to 2019, our research team conducted field surveys about tailings in China, and has gathered some preliminary information of the tailings. The remaining TPs were extracted from the hyper

Land coverage of the tailings wastes

The present study detected a total of 5189 TPs in China. In terms of province, the descending order of them is Hebei (1353), Liaoning (513), Inner Mongolia (344), and Jiangxi (323). By contrast, TPs numbers in Chongqing (7), Beijing (9), and Tibet (10) are relatively small; while none was detected in Taiwan, Shanghai and Ningxia (Table 2).

The accumulated land coverage of TPs in China is about 1884.0 km2, with the average size of 0.363 km2. The tailings' horizontal density with range from 0.009

Conclusion

The key findings of this paper are:

  • (1)

    Present study detected 5189 TPs in China. The average altitude is about 699.4. They occupied a total land size of 1884.0 km2, with the average size of 0.363 km2.

  • (2)

    The TPs are widely distributed throughout the country. In particular, the distribute density of TPs ranging from 0.009 to 0.05/km2, are located in the northern Hebei Province, Liaodong Peninsula, Shandong Peninsula and western Henan province.

  • (3)

    The perimeters of TPs range from 199.6 m to 43,762.0 m, which

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.

Acknowledgement

The project was financially supported by the project of 2016YFC0600604.

References (24)

  • Q.I. Jinping et al.

    Isotope geochemistry and ore genesis of the Qiyugou Gold Deposit, Henan: a synthesis

    Geol. Rev.

    (2007)
  • G.A. Le et al.

    In situ effects of metal contamination from former uranium mining sites on the health of the three-spined stickleback (Gasterosteus aculeatus, L.)

    Ecotoxicology

    (2016)
  • Cited by (40)

    • Disentangling biogeographic and underlying assembly patterns of fungal communities in metalliferous mining and smelting soils

      2022, Science of the Total Environment
      Citation Excerpt :

      Mining and smelting manufacturing extracts valuable components but bringing considerable hazardous by-products such as tailings and slags, which are always deposited directly onto the proximity of land sites (Giongo et al., 2020; Wu et al., 2022). Over 8000 mining and smelting associated enterprises generate billions tons of tailings and slags in recent decades in China (Sun et al., 2020; Tang et al., 2020). Characterized by fine-grained debris, these by-products generally incite high content of metal(loid)s, which can be transferred to adjacent compartments via runoff or atmospheric deposition (Gallego et al., 2021; Liu et al., 2022b; Ran et al., 2021).

    View all citing articles on Scopus
    View full text