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Mine Site Restoration Using Silvicultural Approach

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Abstract

Tree plantations remain to be a viable option for reclamation of abandoned mine lands, either as a use-only method or as a polishing procedure to be used as an add-up technology at already restored sites. It permits restoration of sites by conserving and improving basic soil biological and physical properties. At the same time it is cost-effective and can even bring some economical return through commercial valorization of obtained biomass and aesthetic recovery of the landscape. Its application should be advised more for moderate to low contaminated sites, otherwise the period of restoration could last for decades. This technology is in continuous development providing new possibilities but also some important restrictions in its potential applications. Additional modifications such as adding different amendments like chelating agents or acidifying amendments, organic fertilizers or composts could significantly improve soil properties and thus increase the efficiency of the remediation process. New horizons in the area are emerging by further development of transgenic plants as improved tools for the restoration process, and also by new nanomaterials applied to different plant commercial species
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Bio-Geotechnologies for Mine Site Rehabilitation. http://dx.doi.org/10.1016/B978-0-12-812986-9.00007-5
Copyright © 2018 Elsevier Inc. All rights reserved.
CHAPTER
MINE SITE RESTORATION
USING SILVICULTURAL
APPROACH
Milan Borišev, Slobodanka Pajević, Nataša Nikolić, Andrej Pilipović,
Danijela Arsenov, Milan Župunski
University of Novi Sad, Novi Sad, Serbia
7
7.1 INTRODUCTION
Among various ways that mankind affects environment, surface mining presents one of the most
extreme technologies. Surface mining results in the excavation of different materials such as coal,
metals, minerals and peat, and soil and rock overlying or hosting a shallow ore during which deposit
is physically removed to access the resource (Lima et al., 2016). Hence, opencast coal mining dam-
ages 2–11 times more land than underground mining (Bai et al., 1999). According to various authors
(Miller and Zegre, 2014; Mummey et al., 2002a), surface mining disturbs the landscape; impacts
habitat integrity, environmental flows, and ecosystem functions; and raises concerns about water, air,
and soil quality and often, public health. Overburden dumps created for the accommodation of mine
waste have major effects such as deterioration of aesthetics and reduction in land productivity.
Complete destruction of landform (landscape) and habitat acts as a continuous source of air and
water pollution (Mukhopadhyay et al., 2013). Concerning the mining activities, presently mines are
specifically designed with mitigation methods to manage potential environmental impacts; however,
in former mines the extracted mineral deposits may remain after mines have been abandoned and
usually become a large and uncontrolled source of metal and metalloid contamination (Moreno-
Jiménez et al., 2011). Therefore, to reduce the environmental risks of mining waste, revegеtation has
been recommended as the most promising approach (Bradshaw and Johnson, 1992). Fortunately,
unlike other industries, mining is a temporary user of a specific land site, and proper reclamation can
restore the productivity of land and may bring better landscape (Maiti, 2013). Afforestation of mine
wastes by the establishment of permanent plant cover is an alternative practice for remediation
(Kramer et al., 2000; Mains et al., 2006), rather than to abandon sites or give physicochemical treat-
ment (Ortega-Larrocea et al., 2010). Depending on the type of surface mining, technologies used,
type of the material excavated, and the overall impact on the environment and expected end-point,
the biological recovery activities, according to Lima et al. (2016), can be defined as R4 terminology:
(1) remediation (cleaning of particular target, i.e., soil, water, health with decontamination as end
target), (2) reclamation (recovering ecosystem services, but not all, use of other species), (3) restora-
tion (bring back preexisting ecosystem), and (4) rehabilitation (land management for some uses such
as agriculture, forestry, or urbanization).
... Moreover, using tree species for reclamation treatment is one of the oldest methods used in reclamation, especially in areas under an open cast mining method. Afforestation's influence on soil format is a process for the evolution of a postmining ecosystem [25,26]. Additionally, the afforestation of degraded areas with diverse tree species allows for sequestering more carbon, is more resistant, and gives a bigger biomass production [21,25]. ...
... Afforestation's influence on soil format is a process for the evolution of a postmining ecosystem [25,26]. Additionally, the afforestation of degraded areas with diverse tree species allows for sequestering more carbon, is more resistant, and gives a bigger biomass production [21,25]. Some tree species (pioneer species) are resistant to heavy conditions by using a mechanism against the stressful conditions that occur in degraded areas [25]. ...
... Additionally, the afforestation of degraded areas with diverse tree species allows for sequestering more carbon, is more resistant, and gives a bigger biomass production [21,25]. Some tree species (pioneer species) are resistant to heavy conditions by using a mechanism against the stressful conditions that occur in degraded areas [25]. Soil is a crucial element, and has the ability to influence restored and newly created ecosystems [21]. ...
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This paper investigates the possibility of using fusion Sentinel-2 imageries (2016, ESA) and light detection and ranging (LiDAR) point clouds for the automation of land cover mapping with a primary focus on detecting and monitoring afforested areas and deriving precise information about the spatial (2D and 3D) characteristics of vegetation for reclaimed areas. The study was carried out for reclaimed areas – two former sulfur mines located in Southeast Poland, namely, Jeziórko, where 216.5 ha of afforested area was reclaimed after borehole exploitation, and Machów, where 871.7 ha of dump area was reclaimed after open cast strip mining. The current land use and land cover (LULC) classes at the Machów and Jeziórko former sulfur mines are derived based on Sentinel-2 image processing, and confirmed the applied type of reclamation for both analysed areas. The following LULC classes showed a significant spatial range: broad-leaved forest, coniferous forest, and transitional woodland shrub. The progress of afforested areas, not only in terms of the occupied area, but also in terms of the growth of trees and shrubs, was confirmed. The results of the study showed differences in vegetation parameters, namely, height and canopy cover. Various stages of vegetation growth were also observed. This indicates an ongoing process of vegetation development, as an effect of the reclamation treatment for these areas.
... Unfavorable conditions for plant growth at mining sites present the most crucial limitation in using revegetation for soil remediation (Mulligan et al., 2001). In particular, contamination levels, low-soil fertility, lack of organic matter, disturbance of soil chemical and physical properties, and disappearance of soil microbiota comprise the most common obstacles in revegetation (Borišev et al., 2018). Considering these limitations, selection of proper plant species (and genotypes, where applicable) is a prerequisite for future success of surface mine reclamation. ...
Chapter
Anthropogenic activities worldwide have caused ecological degradation that has resulted in the need to mitigate damage to essential ecosystem services in rural and urban areas. Plant-based technologies, such as phytoremediation and associated phytotechnologies, are ideal for such applications but require extensive knowledge of soil–plant interactions for restoration to be successful. Here we describe remediation of contaminated soils using plants, focusing on the selection of appropriate plant materials and soil factors important for designing remediation systems. The last section of the chapter contains five real-world examples of such systems, including (1) grasslands used for phytoremediation of soil phosphorus, (2) urban afforestation used to create forests in cities, (3) riparian buffer systems used to reduce agrichemical transport from agroecosystems, (4) short rotation woody crops used to enhance ecosystem services at landfills, and (5) woody species used for surface mine reclamation.
... The negative impact of mining disturbance on the surrounding area exceeded 10-15 times the area of mine sites. Tree planting remains one of the most effective strategies in re-establishing ecosystems [4][5][6][7][8] Forest reclamation and restoration of mine sites helps to prevent erosion and to return the land to productive capability [9]. ...
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The study sites is located in an iron-mining district of European part of Russia, called The Kursk Magnetic Anomaly. Birch tree (Betula pendula Roth) plantation was created in 1972 in two different types of heap dumps (hydraulic-mine dumps and mining dumps). Afforested dumps are mainly consisted of cenomanian and aptian sands with the admixture of mesozoic carbonate rocks. In particular hydraulic-mine dumps are formed with sand material and mining dumps are formed with sandy-lime material. For improving poor properties of sand substrate before the planting birch trees on hydraulic-mine dumps were used the technique of soil transfer. The re-spreading fertile layer of soil varies from 30 to 80 cm. Substrate quality varied considerably. Long-term growth and survival of birch tree were analyzed and volume per ha were calculated in different slope parts. Study results show that double-layer substrate with fertile layer (30-40 cm) on the top would not appear to be the best way to rehabilitate mine ecosystems and it has significant disadvantages. At the age of 38 years, common birch is characterized by sufficiently high growth parameters, but low survival.
... At present, the greatest attention is paid to agricultural land reclamation. Grain and legume crops are grown on the open-air lands, perennial grasses are sown, and garden agro-crops are created [9,10]. Since mining activity negatively affects the physical and chemical properties of the soil and the survival of plants, their restoration can be achieved by using such plant species that are able to tolerate specific soil properties within the mine workings. ...
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