Journals / Turkish Journal of Zoology / 2018 / Cilt: 42 - Sayı: 3

Composition and structure of soil fauna community in the Dexing Copper Mine tailings pool after revegetation

Pages
307–315
Publication Date
2018-05-04
DOI
—
🏛️Bibliographic metadata and full text access for this article are provided via DergiPark.
DergiPark Record ↗
✨

AI Summary & Key Takeaways

AI Insight
⚡ TL;DR(Too Long; Didn't Read)

These results should help in improved handling of the environmental issues associated with mines.

📌 3 Key Takeaways

🎯
Objective & Hypothesis:The Dexing Copper Mine is one of the largest copper mines in Asia, but few studies have reported the soil fauna community composition after revegetation.
📊
Key Findings & Data:This study investigated the influence of revegetation on the soil fauna communities and structures in three vegetation restoration models (designated as I, II, and III) and in a sample without revegetation (IV) in two tailings pools of Dexing Copper Mines 1 and 2 using modified Tullgren and Baermann methods.
💡
Conclusion & Impact:These results should help in improved handling of the environmental issues associated with mines.
🔬Design:Lab & Field Experiment
📍Scope:Comprehensive Sample
⚙️Variables:Dominant group · community diversity · functional group

Abstract

The Dexing Copper Mine is one of the largest copper mines in Asia, but few studies have reported the soil fauna community composition after revegetation. This study investigated the influence of revegetation on the soil fauna communities and structures in three vegetation restoration models (designated as I, II, and III) and in a sample without revegetation (IV) in two tailings pools of Dexing Copper Mines 1 and 2 using modified Tullgren and Baermann methods. A total of 548 individuals were collected, which belonged to 5 classes, 7 orders, 3 suborders, and 19 families. The individuals, groups, and diversity of the soil fauna were significantly affected by the vegetation restoration model. In comparison to the sample without revegetation, the samples with revegetation showed a significant increase in the number of individuals and groups of soil fauna (P < 0.01) and significantly increased functional groups of the soil fauna community (P < 0.05). The number of individuals and groups of soil fauna were the highest in sample III, which was planted with trees and covered with guest soil, and the functional groups of the soil fauna community were the highest in samples II and III, which were both covered with guest soil. In principal component analysis, a significant difference was detected in the communities of soil fauna after revegetation, and the structures of soil fauna communities were similar in samples I and IV, which were not covered with guest soil. The number of individuals and groups of soil fauna was closely related to the revegetation in the Dexing Copper Mine tailings pool. These results should help in improved handling of the environmental issues associated with mines.

🔖

Cite This Article

LU, P., DAI, N., SUN, X., ZHANG, G., XU, D., ZHAN, Y. (2018). Composition and structure of soil fauna community in the Dexing Copper Mine tailings pool after revegetation. Turkish Journal of Zoology, Cilt: 42 - Sayı: 3, 307–315. https://ajindex.com/articles/176791

📄 Full Text PDF Viewer

📄

PDF görüntüleyici hazırlanıyor...

References (10)

  1. Asensio V, Covelo EF, Kandeler E (2013). Soil management of copper mine tailing soils—sludge amendment and tree vegetation could improve biological soil quality. Sci Total Environ 456: 82-90.
  2. Berndtsson R, Nodomi K, Yasuda H, Persson T, Chen HS, Jinno K (1996). Soil water and temperature patterns in an arid desert dune sand. J Hydrol 185: 221-240.
  3. Birkhofer K, Bezemer TM, Bloem J, Bonkowski M, Christensen S, Dubois D, Ekelund F, Fließbach A, Gunst L, Hedlund K et al. (2008). Long-term organic farming fosters below and aboveground biota: implications for soil quality, biological control and productivity. Soil Biol Biochem 40: 2297-2308.
  4. Carrillo Y, Ball BA, Bradford MA, Jordan CF, Molina M (2011). Soil fauna alter the effects of litter composition on nitrogen cycling in a mineral soil. Soil Biol Biochem 43: 1440-1449.
  5. Chen F, Yao Q, Tian JY (2016). Review of ecological restoration technology for mine tailings in China. Eng Rev 36: 115-121.
  6. Chen HM, Zheng CR, Zhou DM, Tu C, Gao L (2005). Changes in soil fertility and extractable heavy metals in Dexing copper mine tailing pool after revegetation. Acta Pedologica Sinica 42: 29-36 (in Chinese). Cristescu RH, Frère C, Banks PB (2012). A review of fauna in mine rehabilitation in Australia: current state and future directions. Biol Conserv 149: 60-72. Decaëns T, Lavelle P (2011). Soil fauna diversity and ecosystem functions in grasslands. In: Lemaire G, Hodgson J, Chabbi A, editors. Grassland Productivity and Ecosystem Services. Wallingford, UK: CAB International, pp. 166-176.
  7. Escobar IEC, Santos VM, da Silva DKA, Fernandes MF, Cavalcante UMT, Maia LC (2015). Changes in microbial community structure and soil biological properties in mined dune areas during re-vegetation. Environ Manag 55: 1433-1445.
  8. Frouz J, Elhottová D, Pižl V, Tajovský K, Šourková M, Picek T, Malý S (2007). The effect of litter quality and soil faunal composition on organic matter dynamics in post-mining soil: a laboratory study. Appl Soil Ecol 37: 72-80.
  9. Ge BM, Zhang DZ, Cui J, Jiang SH, Tong XH, Zhou CL, Tang BP (2016). Impact of dike age on biodiversity and functional composition of soil macrofaunal communities in poplar forests in a reclaimed coastal area. Turk J Zool 40: 241-247.
  10. Ge F, Liu XH, Pan WD, Gao L, Zeng YP, Jiang BZ (2011). The role of earthworm in the ecological restoration of mining wasteland of Dexing Copper Mine in China. Acta Ecological Sinica 21: 1790-1795 (in Chinese). Korboulewsky N, Perez G, Chauvat M (2016). How tree div