Abstract
The COVID-19 epidemic, food and water insecurity, and the climate emergency have impacted the lives of billions of people worldwide. Ecosystems play a crucial role in tackling these problems. Hence, it is a prime necessity to keep the ecosystems safe and sustainably manage the resources. But this would not suffice for the protection and sustainable management of our surviving natural landscapes and oceans; we also need to restore the planet’s devastated ecosystems and the enormous benefits they give. Mining exerts a lot of pressure on the land resources further depleting the fertility of the soil. The overburdened dumps are devoid of the nutrients which turns natural succession at a slow pace. The restoration of the degraded mined areas is essential to re-establish the ecological balance so that a self-sustaining ecosystem can be maintained. The plantation of selected species of plants could be a sustainable and organic tool for the restoration of the degraded mined land. In today’s context, various ways regarding ecological restoration are suggested, but the native plant species plantation is the best tool for restoring the degraded land at a quicker pace. The present paper reviews the importance of the native plant species and their efficacy in restoring degraded mined land based on area and time of succession and climax.
Similar content being viewed by others
Explore related subjects
Discover the latest articles, news and stories from top researchers in related subjects.Avoid common mistakes on your manuscript.
1 Introduction
In the current era, the degradation of an environment is linked with the developmental activities and unconsciousness of people about maintaining the ecological balance of the Earth. Humans since pre-historic times utilized natural resources for their comfort despite of their limited availability. Naturalization of humans has turned into the humanization of nature eventually changing the very existence of repletion of both biotic and abiotic resources. Mining of important elements from Earth’s crust is an old phenomenon which eventually turns it into barren nutrient less land. The restoration of such drastically disturbed mined lands had always achieved a great significance throughout the world. The process of restoration has become an integral part of the developmental processes around the globe (Maiti and Ahirwal 2019).
Human activities in the name of development have changed Earth’s surface and ecosystems the most in recent decades (Hu et al. 2020), and mining, like most human livelihoods, has had the greatest impact on ecosystem structure and function (Gabarron et al. 2018; Luna et al. 2018). Mining regions often experience severe environmental deterioration, including vegetation loss, soil erosion, and quality reduction (Karaca et al. 2018). Certain measures like tree planting, agricultural reclamation, and other vegetation restoration programs can speed up soil repair and increase the biological richness of land degraded by mining (Hou et al. 2019). The damage which is caused by mining is tabulated in Table 1.
2 Significance of Soil Restoration
Soil restoration is the most important and foremost step in ecological restoration. Soil being one of the limited resources available to mankind, it needs proper attention during ecological restoration as it takes thousands of years for soil to restore its fertility. Some environmental, natural, and anthropogenic factors directly or indirectly affect the soil. Climate change and global warming affect the decomposition pattern and nutrient cycling. Besides these, natural disturbances like floods, drought, and landslides also add to soil degradation (Williams et al. 2020). Some anthropogenic factors which drastically affect the soil are mentioned in Fig. 1.
Soil health indicators include soil organic matter, total nutrient elemental concentration, available nutrient elemental concentration, pH, and electrical conductivity. Plant recolonization and establishment depend upon the physical, chemical, and biological (nutrient) support from the soil health (Shrestha et al. 2019). Vegetation restoration improves soil conditions making it conducive for species colonization and ecosystem development by increasing soil organic matter and nutrients (Kumar et al. 2015). To forecast vegetation restoration status and soil conditions, humans must understand the likely changes in soil organic matter content and nutrient proportion throughout the restoration period.
Revegetation in arid environments is one of the best approaches to improve the soil quality and address ecological restoration (Li and Liber 2018). However, very few plant species can thrive in degraded mined lands due to the scarce availability of soil nutrients and the high degree of metal toxicity (Wang et al. 2018). Furthermore, choosing promising plants is challenging when biological invasion concerns are considered because invasive species suppresses the growth of native plant species which leads to low biodiversity and an unstable environment (Bauman et al. 2015). For speedy restoration of degraded mined lands, the use of native plant species may be the optimal tool to wade off the threat of invasive and alien species.
The mining sector is an important sector and is related to the development of a country. But mining brings deterioration of environmental entities along with it. The degradation of soil is an unavoidable issue which accompanies mining activities. Deforestation, soil erosion, and overburdened dumps are the consequences of mining. Post the mining process, the lands get degraded which if left as such will take many decades to reach the climax stage of ecological succession. The challenging task in ecological restoration is the soil restoration which can be carried out through the plantation of species preferably native plant species for faster growth and reclamation of land.
Ecosystem reconstruction—restoring the land’s ability to capture and retain resources—is the main objective of mined land restoration. Ecosystem restoration can stop degradation, increase ecosystem utility, and restore biodiversity. Ecosystems and species loss harm people and the environment. Ecosystem service decrease might cost $10 trillion in global GDP by 2050. Thirty-three percent of commercial fish stocks are overfished, threatening over 60 million fishermen worldwide (FAO 2020). Fresh water supports 1.4 billion livelihoods, including food, energy, and water (United Nations 2018). A healthy and productive ecosystem is required to reap environmental, economic, and social advantages to its optimum. Ecosystem restoration can stop degradation, increase ecosystem utility, and restore biodiversity (Strassburg 2020). Figure 2 shows the need for ecological restoration of degraded mined lands.
Though mineral extraction and utilization in any country are pertinent to boost up its economy, yet in the same context, maintenance of the ecosystem is equally important for the subsistence of life on this planet earth. After mining the overburdened dumps do not support any vegetation, here arises the necessity for human intervention to restore such degraded mined lands. Knowledge on the adaptability of different plant species and their role in nutrient dynamics is vital to indulge in restoration measures through biological means (Gairola 2014).
Margenau et al. (2019) suggested plantation of native plant species accelerates the forest succession on degraded mined lands. The restoration of the degraded mine sites includes the control of all types of disturbances of soil, i.e., physical, chemical, and biological. Various factors like the pH of soil, fertility of soil, and soil microbial community which makes the degraded soil productive need to be monitored for better results. Revegetation with native species has been the oldest yet an effective process for restoration of the degraded lands (Gairola 2014).
2.1 Importance of Plantation in Degraded Mined Lands
The mining methods, height, slope of the overburdened piles, the nature of the mine soil, and the geo-climatic conditions are not only the factors on which the success of the mined soil recovery depends but in addition to these factors like the choice of plant species selected for reclamation/restoration of the mined land plays a key role (Pinto et al. 2020). Ahirwal and Pandey (2020), in their study, focused on the selective plantation of the species which can withhold the stress conditions, climate resilience, and moreover be native to the study area. The restoration success depends on the selection of plant species and various soil amendments made so that the topsoil productivity can be enhanced and degraded mined areas can be recovered and restored quickly. Gordana et al. 2019 studied the importance of vegetation on the fly ash deposits generated from coal combustion by using native plant species. The reason for the selection of native plant species is its best adaptation to the local environment and boosting up the ecorestoration management. Native species can tolerate the harsh weather condition thereby increasing the chances of thriving on degraded areas as stable plant communities. Table 2 describes the important studies taken worldwide on the importance of plantation in degraded lands and their major outcomes.
Pietrzykowski (2019) emphasized that for ensuring landscape and environmental profits of degraded mined lands, restoration and establishment of a sustainable ecosystem are necessary. The plantation of tree species on the reclaimed mined soil is significant, because the success of restoration depends on the selection and adaptation of tree species on the degraded mined lands. Figure 3 shows the impact of ecological restoration on the environment.
Buta et al. (2019) aimed at developing the strategy on the eco-restoration of degraded mined land in the northwestern part of Transylvania (Romania). The soil quality was improved overall with the increasing years of restoration. The results showed the revegetation in the abandoned and degraded mined land had brought out considerable changes in soil quality. The ecological integrity and self-sustainability of the degraded mined land were restored with the help of revegetation.
Swab et al. (2017) studied many species in combination with prairie species making a standard reclamation mix. The prairie species were used as they were native species of North America and were most helpful in creating higher diversity plantation in the three mined sites in South Eastern part of Ohio. Mishra and Patra (2017) found that the native plant species were helpful for faster restoration of the degraded mined land with initially few human facilitation and then naturally.
Pioneer species mainly the hardy plants, algae, or moss occupies the degraded area as they are able to survive in a hostile environment. They are the first species which returns to the degraded lands. During the restoration of degraded mined lands, emphasis shall be on planting the native species as it fulfills the restoration and reforestation objectives. Native species suits best for the restoration process. The use of native plant species in the ecorestoration process restores the socio-economic gains, and it enhances the environmental gains also, in the form of soil and water retention. It also helps in carbon sequestration and enhances the ecological succession in a degraded area. Figure 4 represents the steps which leads to ecological succession in degraded lands. Some of the major studies which have been undertaken by various researchers are tabulated in Table 3 with the outcome of their studies.
3 Restoration of Degraded Land Sustainably
The goal of the “Decade on Ecosystem Restoration,” which the United Nations has designated to run from 2021 to 2030, is to restore damaged landscapes so they may once again support human livelihoods, mitigate the effects of climate change, and increase biodiversity. Restoring healthy ecosystems may benefit land and people, promoting biodiversity and stimulating economic growth—both now and after the pandemic, in a sustainable fashion when both environment and economic resiliency are urgently needed. Mansuy (2020) concluded that a chance to restore degraded landscapes and provide co-benefits, such as livelihoods and commercial prospects, is by investing in restoration. In India, 29% (96.4 million hectares) of land is degraded. India became the part of “Bonn Challenge” which is a global effort to restore the world’s degraded lands (approximately 150 million hectares) till 2020 and approximately 350 million hectares by the year 2030. While the challenge is a tougher one, therefore, a systematic planning is required for restoring vast amounts of degraded lands (The Hindu 2020).
In the current scenario, the plantation of the native species seems the best possible way not only to restore the degraded land but also to the onset of ecosystem functions and ecosystem services sooner. Singh et al. (2019) in their study discussed about the success of bioenergy plantation in degraded lands. Biofuels are the genetically engineered bioenergy crops which have the capability of growing in stressful conditions and can increase the soil fertility. On the other hand, the consumption of crude oil is increasing at a faster pace. Therefore, the biofuel plantation on the degraded lands can be a solution for solving the problem of energy crises and accelerate the restoration of degraded lands in a sustainable way.
4 Role of Degraded Mined Land Restoration in Mitigating Climate Change
The importance of physical features of restoration, the choice of plant species for biological restoration, and their combined impact on creating socioeconomic and environmental advantages are highlighted through practical approaches that are feasible for ecosystem restoration. Ahirwal and Maiti (2021) advise including a site-specific restoration strategy, using native plants for replanting, and including the neighborhood in restoration initiatives. In addition, they are crucial for achieving the UN-Sustainable Development Goals (UN-SDGs), which include eradicating poverty and hunger, supplying affordable and clean energy, reducing global warming, and restoring life to damaged lands. Some of the impacts are shown in Fig. 5.
Mining and related activities severely disrupt the terrestrial ecology, causing significant land degradation and a crisis in the global climate. The formation of ecosystems and improved SOC sequestration are possible as a result of soil restoration techniques in mine wastes. Reclaiming mine waste increases soil horizon development rather quickly, which increases carbon sequestration capacity. As a result, reclaimed soil serves as a significant sink for atmospheric CO2. Though initially quite low when compared to undisturbed soils, the SOC content of restored mine soil steadily rises with the age of the revegetation.
The productivity of land uses developed on reclaimed areas and the properties of technosols determine the rate of carbon sequestration. Mine soils therefore have a great potential to increase their C capital. The accumulation and the current level of carbon in the soil determine a soil ‘s capacity to sequester carbon (Bandyopadhyay and Maiti 2022). Figure 6 depicts the customary practice of ecological restoration.
Ecological restoration can serve as a genuine climate change adaptation strategy because the plant it produces has a long lifespan and does not require ongoing maintenance (Lim et al. 2022). Degraded lands not only negatively affect the ecosystem services but also adversely affect the livelihood of the people. According to a published study, the restoration efforts in 15% of the total degraded lands in the world can prevent approximately 60% of extinction, and approximately 299 gigatonnes of carbon dioxide can be soaked up which has increased since the onset of industrial revolution. The study further reveals that 70% of the birds, amphibians, and mammals can be saved from the risk of extinction, provided 30% of the world’s degraded lands are restored to their original condition, and additional 465 billion tons of carbon dioxide will be sequestered (Strassburg 2020). The degraded mined lands if restored efficiently can act as a carbon sink for greenhouse gases. The process of reclamation is a significant part of mining operation which aims to stabilize degraded mine sites and also results in carbon sequestration. The restored land can act as a carbon sink and can also contribute potentially to the future carbon credit commodity.
5 Future Prospects of Ecorestoration
Active interventions are the need of the hour to stop or reverse ecological function and loss in degraded ecosystems worldwide. Under future climates, restoration may not be enough to reverse habitat loss and restore functions. Restoration could also include primitive steps to strengthen extant populations’ resilience and adaptability to expected future conditions. Adapting lost habitats to future conditions may improve restoration success. In general, restoration in the classic sense of returning a system to a prior state is unlikely to be sufficient or effective under future climates; instead, restoration should strengthen and may redefine populations and species to endure future environmental shocks. According to an online UNEP report, ecosystem services, or the advantages individuals get from ecosystems, are worth more than 10% of global economic production and influence 3.2 billion people or 40% of the world’s population (UNEP 2021).
The world needs to fulfil its current obligations to rehabilitate 1 billion hectares of damaged land. One of the most crucial and viable methods for providing biologically based solutions to issues like food insecurity, climate change, global warming mitigation and adaptation, and biological diversity loss is ecosystem restoration. It would not be quick or simple, and it will require significant adjustments to everything from how we gauge economic growth to how and what we consume. The wonder of ecosystem restoration, however, is that it can take place at any scale, and everyone can play a part.
6 Conclusion
The degraded lands are one of the important contributors to climate change as they lose soil carbon and also emit the GHG’s (Greenhouse Gases). In the current scenario, when the world is combating the problem of climate change, degraded lands can prove to be an asset if restored efficiently. Degraded lands which are lying unutilized, through proper restoration strategy, can become the bigger source of carbon sink. According to an estimate, ecosystem services loss due to the degradation of land is between 6.6 and 10.6 trillion USD annually. (IUCN 2015). Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem (IPBES) reported the reduction of crop yield by 10% globally, and in certain regions, the reduction will be approximately 50% by the year 2050 (SEI 2018).
Thus, the above-mentioned scenario poses to be the biggest threat for us and our future generation, which can worsen if not controlled. The restoration of degraded lands at an extensive scale has become the need of an hour. Turning the degraded land into agricultural land can be a difficult choice, but when a country like India with the second highest population in the world is developing at a faster pace and wants to end up its food insecurity, then turning the reclaimed land into agricultural land seems to be a good option Lei et al. (2016). Many climate-resilient crops which can undertake the abiotic stress like soil infertility and less availability of water can be planted according to the topography of the area. Apart from the plantation of native species, millets can become a suitable option for restoring the fertility of restored sites. Research and development regarding the plantation of millets in the restoration lands is highly required.
Change history
08 March 2023
A Correction to this paper has been published: https://doi.org/10.1007/s42729-023-01204-8
References
Ahirwal J, Maiti SK (2021) Restoring coal mine degraded lands in India for achieving the United Nations-Sustainable Development Goals. Res Ecol 30:13606. https://doi.org/10.1111/rec.13606
Ahirwal J, Pandey VC (2020) Restoration of mine degraded land for sustainable environmental development. Res Ecol 29:4. https://doi.org/10.1111/rec.13268
Bandyopadhyay S, Maiti SK (2022) Steering restoration of coal mining degraded ecosystem to achieve sustainable development goal-13 (climate action): United Nations decade of ecosystem restoration (2021–2030). Environ Sci Pollut Res 29:88383–88409. https://doi.org/10.1007/s11356-022-23699-x
Bauman JM, Cochran C, Chapman J, Gilland K (2015) Plant community development following restoration treatments on a legacy reclaimed mine site. Ecol Eng 83:521–528. https://doi.org/10.1016/j.ecoleng.2015.06.023
Buta M, Blaga G, Paulette L et al (2019) Soil reclamation of abandoned mine lands by revegetation in northwestern part of Transylvania: a 40-year retrospective study. Sustainability 11:3393. https://doi.org/10.3390/su11123393
Food and Agriculture Organization of the United Nations (2020) Report on The State of World Fisheries and Aquaculture Sustainability in action (Rome, 2020) 54. https://doi.org/10.4060/ca9229en
Gabarron M, Faz A, Martinez-Martinez S, Acosta JA (2018) Change in metals and arsenic distribution in soil and their bioavailability beside old tailing ponds. J Environ Manag 212:292–300. https://doi.org/10.1016/j.jenvman.2018.02.010
Gairola SU (2014) Soil chemical properties in an age series of restored mined land-a case study from Uttarkhand, India. Soil Environ 33:38–42
Gastauer M, Ramos SJ, Caldeira CF, Siqueira JO (2021) Reintroduction of native plants indicates the return of ecosystem services after iron mining at the Urucum Massif. Ecosphere 10:e03762. https://doi.org/10.1002/ecs2.3762
Gordana G, Miroslava M, Pavle P (2019) Ecorestoration of fly ash deposits by native plant species at thermal power stations in Serbia, Editor(s): Vimal Chandra Pandey, Kuldeep Bauddh, Phytomanagement of Polluted Sites, Elsevier, 2019:113–177, ISBN 9780128139127. https://doi.org/10.1016/B978-0-12-813912-7.00004-1.
Hou XY, Liu SL, Cheng FY, Zhang YQ, Dong SK, Su XK, Liu GH (2019) Vegetation community composition along disturbance gradients of four typical open-pit mines in Yunnan Province of southwest China Land Degrad. Dev 30:437–447. https://doi.org/10.1002/ldr.3234
Hu Y, Yu Z, Fang X, Zhang W, Liu J, Zhao F (2020) Influence of mining and vegetation restoration on soil properties in the eastern margin of the Qinghai-Tibet Plateau. Int J Environ Res Public Health 17:4288. https://doi.org/10.3390/ijerph17124288
IUCN (2015) Land degradation and climate change. https://www.iucn.org/resources/issues-briefs/land-degradation-and-climate-change. Accessed 27 June 2022
Karaca O, Cameselle C, Reddy KR (2018) Mine tailing disposal sites: contamination problems, remedial options and phytocaps for sustainable remediation. Rev Environ Sci Biol Technol 17:205–228. https://doi.org/10.1007/s11157-017-9453-y
Kondratenko L, Gura D, Shaidullina V, Rogulin R, Kondrashev S (2022) Restoration of vegetation around mining enterprises. Saudi J of Biol Sci 29:1881–1886. https://doi.org/10.1016/j.sjbs.2021.10.034
Kumar S, Maiti SK, Chaudhuri S (2015) Soil development in 2–21 years old coalmine reclaimed spoil with trees: a case study from Sonepur-Bazari opencast project, Raniganj Coalfield. India Ecol Eng 84:311–324. https://doi.org/10.1016/j.ecoleng.2015.09.043
Lei K, Pan H, Lin C (2016) A landscape approach towards ecological restoration and sustainable development of mining areas. Ecol Eng 90:320–325. https://doi.org/10.1016/j.ecoleng.2016.01.080
Lestari DA, Fiqa AP, Fauziya BS (2019) Growth evaluation of native tree species planted on post coal mining reclamation site in East Kalimantan, Indonesia. Biodiversitas 20:134–143
Lewis S, Rosales J (2020) Restoration of forested lands under Bauxite mining with emphasis on Guyana during the first two decades of the XXI century: a review. J Geosci Environ Prot 8. https://doi.org/10.4236/gep.2020.811003
Li S, Liber K (2018) Influence of different revegetation choices on plant community and soil development nine years after initial planting on a reclaimed coal gob pile in the Shanxi mining area. China Sci Total Environ 618:1314–1323. https://doi.org/10.1016/j.scitotenv.2017.09.252
Lim CH, Lim BS, Kim R, Kim DU, Seol JW (2022) Climate change adaptation through ecological restoration, Editor(s): Manoj Kumar Jhariya, Ram SwaroopMeena, Arnab Banerjee, Surya Nandan Meena, Natural Resources Conservation and Advances for Sustainability, Elsevier, 2022:151-172.https://doi.org/10.1016/B978-0-12-822976-7.00013-2
Lozano-Baez SE, Barrera-Catano JI, Rodrigues RR, Dominguez-Haydar Y, Meli P (2022) Forest restoration after alluvial gold mining can recover vegetation structure. Case Study Colombia, Biota Colomb 23:209
Luna L, Vignozzi N, Miralles I, Sole-Benet A (2018) Organic amendments and mulches modify soil porosity and infiltration in semiarid mine soils. Land Degrad Dev 29:1019–1030. https://doi.org/10.1002/ldr.2830
Maiti SK, Ahirwal J (2019) Ecological restoration of coal mine degraded lands: topsoil management, pedogenesis, carbon sequestration, and mine pit limnology, Chapter 3 Editor(s): Vimal Chandra Pandey, Kuldeep Bauddh, Phytomanagement of Polluted Sites, Elsevier, 83–111, ISBN 9780128139127, https://doi.org/10.1016/B978-0-12-813912-7.00003-X
Maiti SK, Bandyopadhyay S, Mukhopadhyay S (2021) Importance of selection of plant species for successful ecological restoration program in coal mine degraded land, Editor(s): Kuldeep Bauddh, John Korstad, Pallavi Sharma, Phytorestoration of Abandoned Mining and Oil Drilling Sites, Elsevier, 2021:325-357.https://doi.org/10.1016/B978-0-12-821200-4.00014-5
Mansuy N (2020) Stimulating post-COVID-19 green recovery by investing in ecological restoration. Restor Ecol 28:1343–1347. https://doi.org/10.1111/rec.13296
Margenau EL, Wood PB, Weakland CA, Brown DJ (2019) Trade-offs relating to grassland and forest mine reclamation approaches in the central Appalachian region and implications for the songbird community. Avian Conserv Ecol 14 https://doi.org/10.5751/ACE-01304-140102
Mishra RK, Behera BK, Dash A, Patra BK (2021) Ecological restoration of degraded habitats of Jajang Iron and Manganese Ore Mines, Keonjhar, Odisha, India. In (Ed.). Environ Manag-Pollut, Habitat, Ecol, Sustain. IntechOpen. https://doi.org/10.5772/intechopen.99584
Mishra RK, Patra BK (2017) Vegetation analysis: a tool for restoration of degraded habitats of Raikela Iron Ore Mines Sundergarh, Odisha. Int J Environ Sci Nat Res 5:555674. https://doi.org/10.19080/IJESNR.2017.05.555674
Nguyen HX, Tran HT, Pham HTT (2020) Land improvement solutions: afforestation and planting fruit trees and short-term crops after mine closure in Luong Son District, HoaBinh Province, Vietnam. Appl and Environ Soil Sci 2020:5189497. https://doi.org/10.1155/2020/5189497
Pandey VC, Rai A, Singh L et al (2022) Understanding the role of litter decomposition in restoration of fly ash ecosystem. Bull Environ Contam Toxicol 108:389–395. https://doi.org/10.1007/s00128-020-02994-8
Pietrzykowski M (2019) Tree species selection and reaction to mine soil reconstructed at reforested post-mine sites: Central and Eastern European experiences. Ecol Eng :X3:100012(2019) ISSN-2590–2903. https://doi.org/10.1016/j.ecoena.2019.100012
Pinto LFS, Stumpf L, Miguel P (2020) Reclamation of soils degraded by surface coal mining. In: Soni A (ed) Mining techniques- past, present and future. https://doi.org/10.5772/intechopen.93432
Pratiwi, Narendra BH, Siregar CA (2021) Managing and reforesting degraded post-mining landscape in Indonesia: a review. Land 10:658. https://doi.org/10.3390/land10060658
Roy R, Sultana S, Wang J, Mostofa MG (2022) Revegetation of coal mine degraded arid areas: the role of a native woody species under optimum water and nutrient resources. Environ Res 204:111921. https://doi.org/10.1016/j.envres.2021.111921
Sawarkar R, Shakeel A, Kokate PA, Singh L (2023) Organic wastes augment the eco-restoration potential of bamboo species on fly ash-degraded land: a field study. Sustainability 15:755. https://doi.org/10.3390/su15010755
SEI (2018) Land degradation worsening climate change and undermining well-being of billions. https://www.sei.org/featured/ipbes-land-degradation/. Accessed 27 June 2022
Shrestha P, Gautam R, Ashwath N (2019) Effects of agronomic treatments on functional diversity of soil microbial community and microbial activity in a revegetated coal mine spoil. Geoderma 338:40–47. https://doi.org/10.1016/j.geoderma.2018.11.038
Singh S, Kumar D, Jaiswal R, Mukherjee KA, Verma JP (2019) Restoration of degraded lands through bioenergy plantations. Restor Ecol 28:263–266. https://doi.org/10.1111/rec.13095
Song L, Qian J, Zhang F, Kong X, Li H (2022) An ecological remediation model combining optimal substrate amelioration and native hyperaccumulator colonization in non-ferrous metal tailings pond. J Environ Manage 322:116141. https://doi.org/10.1016/j.jenvman.2022.116141
Strassburg BBN (2020) Global priority areas for ecosystem restoration. Nature 586(7831):724–729. https://doi.org/10.1038/s41586-020-2784-9
Swab R, Lorenz N, Byrd S, Dick R (2017) Native vegetation in reclamation: improving habitat and ecosystem function through using prairie species in mine land reclamation. Ecol Eng 108:525–536. https://doi.org/10.1016/j.ecoleng.2017.05.012
The Hindu (2020) India to rejuvenate 50,000 hectares of degraded land. https://www.thehindu.com/sci-tech/energy-and-environment/india-to-restore-50-lakh-hectares-of-degraded-land-by-2030 - . Accessed 18 June 2022
UNEP (2021) Report on ecosystem restoration for people, nature and climate. www.unep.org/resources/ecosystem-restoration-people-nature-climate. Accessed 24 June 2022
United Nations Sustainable Development Goal 6 Synthesis Report 2018 on Water and Sanitation. Executive Summary, p. 12. Available via: https://www.unwater.org/app/uploads/2018/05/UN-Water_SDG6_Synthesis_Report_2018_Executive_Summary_ENG.pdf. Accessed 15 June 2022
Wang D, Zhang B, Zhu L, Yang Y, Li M (2018) Soil and vegetation development along a 10-year restoration chronosequence in tailing dams in the Xiaoqinling gold region of Central China. CATENA 167:250–256. https://doi.org/10.1016/j.catena.2018.05.007
Williams MI,Farr CL, Page-Dumroese DS (2020) Soil management and restoration, Pouyat RV et al. For Rangel Soils U S Under Chang Cond. https://doi.org/10.1007/978-3-030-45216-2_8
Yadav S, Pandey VC, Kumar M, Singh L (2022) Plant diversity and ecological potential of naturally colonizing vegetation for ecorestoration of fly ash disposal area. Ecol Eng 176:106533. https://doi.org/10.1016/j.ecoleng.2021.106533
Author information
Authors and Affiliations
Corresponding author
Ethics declarations
Conflict of Interest
The authors declare no competing interests.
Additional information
Publisher's Note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
The original version of this article was revised: The affiliation for Shikha Uniyal Gairola given in this article as originally published was inaccurate and has been corrected.
Rights and permissions
Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law.
About this article
Cite this article
Gairola, S.U., Bahuguna, R. & Bhatt, S.S. Native Plant Species: a Tool for Restoration of Mined Lands. J Soil Sci Plant Nutr 23, 1438–1448 (2023). https://doi.org/10.1007/s42729-023-01181-y
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s42729-023-01181-y