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Guide to post-industrial site restoration and re-establishment of rich communities of plant species for the provision of key ecosystem services
In line with the UN sustainable development goals, Biodiversity and Ecosystem Services on Post-Industrial Land is an expert guide to ecological restoration of post-industrial lands, explaining how to re-introduce biodiversity and ecosystem services by implementing natural processes in the rehabilitation of disturbed sites. It covers both the initial stages associated with the improvement of physicochemical and biological substrate characteristics as a precondition for continuous vegetation, as well as the subsequent re-establishment of rich communities of plant species and how these communities may be optimized for their biodiversity and ecosystem services such as pedogenesis, nutrient cycling, habitation for other organisms, food plants for herbivores, carbon sequestration, and aesthetic value.
Case studies of successful restoration of industrial sites from Asia, Africa, North and South America, and Europe, which include coal and mineral mining sites, oil drilling sites, and dumpsites, complement the conceptual part of the text and demonstrate how to put the theory into practice.
Written by an experienced researcher in the field, Biodiversity and Ecosystem Services on Post-Industrial Land includes information on:
Biodiversity and Ecosystem Services on Post-Industrial Land is an essential guide for environmental managers, scientists, ecologists, and engineers tasked with restoring post-industrial sites, managers in mining, oil, gas, and other heavy industries, and NGOs involved in sustainable land use.
Dr. Vimal Chandra Pandey is a leading researcher in the field of phytomanagement of polluted sites. He is listed in the World's Top 2% Scientists, announced by Stanford University and Elsevier BV. He serves as Editor, Advisory Board and Editorial Board Member for various journals, including Land Degradation and Development; Restoration Ecology; Environment, Development and Sustainability; Ambio; Clean-Soil Air Water; Discover Sustainability; Environmental Management; and Bulletin of Environmental Contamination and Toxicology.
List of Contributors xv
About the Editor xxi
Foreword xxiii
Preface xxv
Acknowledgments xxvii
1 Mining Sustainability: A Reality in Arid Zones 1 Elizabeth J. Lam, Italo L. Montofré, and Fernando A. Alvarez
1.1 Introduction 1
1.2 Mining in Chile 3
1.3 Chile: Arid Zone Mining 6
1.4 Circular Mining and Arid Zone Sustainability 13
1.5 Conclusions 17
References 18
2 Restoring Biodiversity and Ecosystem Services on Post-Industrial Land: Challenges and Opportunities 25 Sameer Shekhar, Shubham Abhishek, Bhanu Pandey, and Siddharth Singh
2.1 Introduction 25
2.2 Post-Industrial Landscapes: A Brief Overview 26
2.3 Biodiversity on Post-Industrial Land 28
2.4 Ecosystem Services on Post-Industrial Land 30
2.5 Restoring Biodiversity and Ecosystem Services on Post-Industrial Land 34
2.6 Policy and Management for Post-Industrial Landscapes 37
2.7 Key Findings and Implications 41
2.8 Challenges and Future Research Directions 41
2.9 Conclusion 43
References 43
3 Spontaneous Flora on Post-industrial Metalliferous Sites 53 Ksenija Jakovljevic, Tomica MiSljenovic, and Dragana Randelovic
3.1 Introduction 53
3.2 Definition and Types of Post-industrial Sites 54
3.3 Spontaneous Flora: Characteristics and Benefits 63
3.4 Spontaneous Flora in Post-industrial Sites: Current Findings 65
3.5 Ecosystem Services of Spontaneous Flora on Post-industrial Metalliferous Sites 76
3.6 Conclusions 82
Acknowledgments 83
References 83
4 Restoration Ecosystem Toward Spontaneous Succession on Reclaimed Mining Sites 97 Marcin Pietrzykowski, Bartlomiej Wos, Justyna Likus-Cieslik, Marek Pajak, Edyta Sierka, and Barbara Stalmachová
4.1 Introduction 97
4.2 Biodiversity of Succession Communities on Mine Sites 98
4.3 Mine Soil Development Under Reclamation and Successional Communities 104
4.4 Biomass and Wood Productivity Potential of Reclaimed and Successional Plant Communities 106
4.5 Plant Communities from Succession as Indicators of Site Conditions 107
4.6 Managed Succession on Post-Mine Sites 109
4.7 Example of a Reclamation by Using Vegetation Communities from Succession 110
4.8 Conclusion 111
Acknowledgments 112
References 112
5 Plant Diversity on Post-Industrial Land: Resilience and Restoration 119 Shivali Sharma, Jonnada Likhita, Sunny Sharma, Gaurav Sharma, Amit Kumar, Rupesh Kumar, and Vimal Chandra Pandey
5.1 Introduction 119
5.2 Numerous Elements that Promote Industrialization 121
5.3 Industrial Impact on Plant Communities 122
5.4 Effects of Toxins Released by Various Industries 125
5.5 Mechanisms of Plant Resilience 125
5.6 Case Studies 138
5.7 Challenges and Failures 141
5.8 Ecological Restoration 143
5.9 Introduction of Important Species 146
5.10 Success Stories in Restoration 147
5.11 Policy Implications 155
5.12 Conclusion and Ways Forward 157
References 159
6 Plantation Forestry for Ecorestoration: A Working Premises 171 Manoj Kumar Jhariya, Abhishek Raj, Arnab Banerjee, Surendra Singh Bargali, and Kiran Bargali
6.1 Introduction 171
6.2 Plantation Forestry: Global Area Context 173
6.3 Expansion of Plantation Forestry to Industrial Forest Plantation 173
6.4 Species Grown in Forest Plantations 175
6.5 Ecosystem Services Through Plantation Forestry 175
6.6 Plantation Forestry Through a Reforestation Approach 178
6.7 Ecological Restoration and Sustainability 179
6.8 Forest Restoration 180
6.9 Plantation Forestry for Climate Change Mitigation 180
6.10 Socioeconomic Perspective of Restoration 181
6.11 Future Perspective 182
6.12 Conclusion 183
References 183
7 Soil Biodiversity and Plant-Microbes Interactions on Post-Industrial Land 189 Aneta Kowalska and Anna Grobelak
7.1 Loss of Soil Biodiversity on Post-Industrial Land 189
7.2 Biodiversity as an Opportunity for Sustainable Transformation of Mining Regions 190
7.3 Treatments Increasing the Biodiversity of Post-Industrial Soil 191
7.4 Post-Industrial Areas as a Refuge of Biodiversity 192
7.5 Plant-Growth-Promoting Microbes and Their Feasibility for Recultivation of Post-Industrial Lands 193
7.6 Summary and Conclusions 194
Acknowledgments 195
References 195
8 Afforestation of Former Asbestos Mines in Quebec, Canada: An Efficient Nature-Based Climate Solution that also Leads to Gains in Biodiversity 199 Nicolas Bélanger, Laurence Grimond, Rim Khlifa, Simon Bilodeau-Gauthier, and David Rivest
8.1 Introduction 199
8.2 Historical Background of Asbestos Mining in Canada 201
8.3 Typical Ecological Restoration 204
8.4 Afforestation 209
8.5 Carbon Sequestration 220
8.6 Gains in Plant and Faunal Diversity Following Afforestation 224
8.7 Conclusion 230
Acknowledgments 231
References 231
9 Bauxite Mine Restoration and Management 241 Shailesh Kumar Yadav, Arnab Banerjee, Manoj Kumar Jhariya, Abhishek Raj, Surendra Singh Bargali, and Vimal Chandra Pandey
9.1 Introduction 241
9.2 Impact of Bauxite Mining 241
9.3 Approaches Toward Management of the Impact of Bauxite Mining 245
9.4 Restoration Targets and Objectives 246
9.5 Stages of Restoration Planning and Implementation 247
9.6 Restoration Implementation 248
9.7 Sustainable Bauxite Mining 254
9.8 Rehabilitation and Restoration in Surguja - A Case Study from Chhattisgarh, India 254
9.9 Conclusion 256
9.10 Future Directives 256
References 258
10 Role of the Local Government in Re-Use of Post-Industrial Sites in Poland 263 Katarzyna Sadowy
10.1 Introduction 263
10.2 Post-Industrial Sites in Poland 266
10.3 Role of the Voivodeships and Municipalities in the Management of Post-Industrial Areas 272
10.4 Conclusions 281
Acknowledgement 282
References 282
11 Restoration of Ecosystem Services of Endangered Wetlands in Post Oil and Gas Exploration Era in the Niger Delta, Nigeria 285 Aroloye O. Numbere, Victoria C. Obinna, Eberechukwu M. Maduike, and Austin E. Abah
11.1 Introduction 285
11.2 Characterization of Wetlands in the Niger Delta 287
11.3 Impact of Oil and Gas Exploration on Wetlands of the Niger Delta 289
11.4 Sedimentary Environment of the Niger Delta 295
11.5 Causes of Wetland Degradation 297
11.6 Ecosystem Services in a Restored Wetland 300
11.7 Sustainable Management of the Wetland in the Niger Delta 301
11.8 Policy Development of Wetlands in the Niger Delta 302
11.9 Conclusion and Recommendations 304
References 304
12 Carbon Sequestration in Revegetated Coal Mine Soil: A Chronosequence Study in the Gevra Opencast Project, Chhattisgarh, India 307 Preeti Singh, Amlan Kumar Ghosh, Ebhin Masto, Santosh Kumar, and Chandini Pradhan
12.1 Introduction 307
12.2 Analysis and Classification of Organic Residue/Plant Materials: Impacts on Carbon Sequestration in Soil 308
12.3 Litterfall Dynamics, Seasonal Variations, and Implications for Soil Organic Carbon Sequestration 309
12.4 Impact of Plant Litter Quality on Decomposition Rate and Soil Health in Restored Coal Mine Areas of Chhattisgarh, India 309
12.5 Role of Plant-Microbe Interactions in Soil Carbon Sequestration: Insights from Microbial Biomass Carbon Dynamics 310
12.6 Different Pools of Soil Organic Carbon in Restored Mine Soil 312
12.7 Total Organic Carbon, C Stock, and C Sequestration in Reclaimed Mine Soil 313
12.8 Insights from Spectroscopic Analysis on Soil Organic Carbon Characteristics in Restored Mine Soils 317
12.9 Conclusion 322
References 324
13 Ecosystem Services from Rehabilitated Waste Dumpsites 329 ml Dotaniya, CK Dotaniya, Kuldeep Kumar, RK Yadav, RK Doutaniya, HM Meena, DK Yadav, Saurabh Shukla, AO Shirale, and Manju Lata
13.1 Introduction 329
13.2 Different Types of Pollution 332
13.3 Risk Assessment of Metal Pollution 336
13.4 Source of Contamination and Its Identification 337
13.5 Effect on Ecological Services 338
13.6 Important Rehabilitated Waste Dumpsites 340
13.7 Ecosystem Services from Rehabilitated Waste Dumpsites 342
13.8 Improvement in Ecological Services by Improving the Waste Discharge Process 342
13.9 Strategies for Improving Ecological Services 344
13.10 Challenges Faced During Rehabilitation 346
13.11 Conclusions 346
References 347
14 Harnessing Aromatic Plants for Phytoremediation: A Scented Solution for Ecology and Economy 357 Vimal Chandra Pandey, Valeria Ancona, D. D. Tewari, and Sanat Kumar Dwibedi
14.1 Introduction 357
14.2 Aromatic Grasses 358
14.3 Aromatic Grasses and Their Phytoremediation Potential 360
14.4 Manifold Usages of Aromatic Grasses 367
14.5 Aromatic Grasses Rooted in UN-SDGs 368
14.6 Conclusion and Prospects 369
References 372
Index 381
Elizabeth J. Lam1, Italo L. Montofré2,3, and Fernando A. Alvarez4
1 Chemical Engineering Department, Universidad Católica del Norte, Antofagasta, Chile
2 Mining Business School, ENM, Universidad Católica del Norte, Antofagasta, Chile
3 Mining and Metallurgical Engineering Department, Universidad Católica del Norte, Antofagasta, Chile
4 Administration Department, Universidad Católica del Norte, Antofagasta, Chile
Mining, one of man's oldest and most important activities (Dubinski 2013; Candeias et al. 2018), has depended on extracted products since the beginning of civilization. Due to the crucial need for materials for industrial and human development, its participation in the economic structure of mining countries and the global economy has greatly increased in the last few decades, currently being one of the world's main economic activities (Lodhia 2018; Lam et al. 2021).
The mining process is based on the extraction and processing of materials of interest (Whitworth et al. 2022). It consists of consecutive operational stages: prospection; exploration; project assessment, development, and construction; resource production and exploitation; and operational closing. These stages may cause environmental and social impacts (Haddaway et al. 2019).
Ore extraction processes have changed with time, forcing the generation of more efficient processes environmentally and community-friendly. In addition, current trends in the extraction of ore with an increasingly lower grade pose new challenges for waste management, considering the increased number of wastes from mining units. This decreased ore grade is accompanied by a tendency to make new explorations and start new mining operations to balance decreased production, by further extracting and processing ore. This results in increased ore drilling, loading, and transport, thus increasing concentrator capacity and leaching processes. Also, low-grade ore makes it necessary to transform it into smaller particles, therefore increasing grinding and its associated energy requirements (Lagos et al. 2018).
Analogically, the production and exploitation stages cause environmental impacts such as industrial emission of sulfur dioxide and nitrogen oxides, high water consumption for industrial processes, and massive mining wastes (MMWs) such as tailings, residues, slags, sterile material, and solid wastes, among others (Lam et al. 2017, 2020a; Zhou et al. 2021). In addition, mine closing has become one of the most important stages on a global basis since a plan is needed from mining companies to mitigate the negative effects of the extractive mining industry, ensuring the physical and chemical stability of installations and mining wastes, according to the legislation on a country basis. In Chile, the closing plan must safeguard people's lives, health, safety, and the environment, according to law 20.551, regulating the closing and post-closing phases of mining sites (Lam et al. 2018).
Impacts from mining processes can be classified into six main groups: (i) soil quality, (ii) flora and fauna, (iii) air quality, (iv) water resources, (v) socioeconomic conditions, and (vi) climate change. These impacts make it necessary to face a series of challenges, even more so when the demand for most minerals may increase in the next few years. In addition, considering sustainable energy transition, the mining industry must create new technological developments to exploit increasingly complex ore bodies, accept the requirement to decrease water and energy resources, optimize waste management in the context of a circular economy (CE), and respond to climate change effects due to increased greenhouse gas emissions (Valenta et al. 2019).
Owing to the spatial distribution of resources, mining activity can be developed in different geographic regions, each of them with particular challenges depending on environmental conditions and the nature of mining activity, considering the type of ore and the processing method. These challenges are particularly relevant in arid zones, where impacts are notorious, considering ecosystem fragility and water scarcity (Liu et al. 2019). For these reasons, the mining industry in arid zones faces different challenges to make production sustainable, particularly the supply of critical agents such as water and energy, along with ecosystem preservation. This challenge is faced by using and controlling sustainability indicators for arid zone mining. At present, many factors could be considered sustainability indicators, such as water consumption, electric and fossil energy consumption, greenhouse gas emissions, land distribution, waste management, and finally, environmental and social impact.
In a different ambit, mining activity evolution has caused an impact on the economic development of many countries such as Chile, where, apart from contributing to the economic development of mining regions, it also influences the development of human beings, who are constantly requiring various mining raw materials and input for creating products and technology for man's progress (Qi 2020). Among mining countries, Chile is a world leader in the production of copper, iodine, rhenium, lithium, molybdenum, boron, silver, and gold (Ministerio de Minería 2022). This brings about great economic benefits, but, on the other hand, it produces a negative environmental impact associated with risks affecting the environment and the population (Castro and Sánchez 2003).
In Chile, mining production became massive in 2001-2015. At the same time, mines aged owing to a decreased ore grade. So, mining activity increased by starting new operations mainly in the country's northern zone, characterized by arid environmental conditions. These zones show scarce rainfall and vegetation, a dry climate, and high differences in temperature between day and night, making it particularly difficult to obtain resources such as water and energy, thus putting ecosystem stability at risk. Hence, sustainable mining must be developed, involving rational natural resource consumption so that annual production cannot jeopardize resources for future generations (Lagos et al. 2018).
Most Chilean mining industries are located in the northern zone, characterized by extreme climatic conditions. Exploitation, apart from economic benefits, has important impacts on the environment and ecosystems. So, it is essential to address future mining by focusing on sustainability, considering three basic pillars: economic, environmental, and social. Therefore, efforts must be directed to actions for maximizing profits, according to available resources, and preserving natural resources for proper ecosystem functioning and equilibrium. Both aspects must be in agreement with the demands and needs of local and surrounding populations, fostering citizen dialog, commitment, and participation in fair and equitable decision-making (Aznar-Sánchez et al. 2019).
Chilean mining produces great volumes of waste, by extracting, using, and processing ore, which is discarded or accumulated, occupying big spaces. It is estimated that more than one million tons of waste from ore concentration and more than two million tons of sterile material are generated daily. The decreased grade of ore deposits currently exploited and those projected requires treating increasingly higher amounts of ore tonnages to keep or increase production levels. In this context, the amount of waste to be disposed of either as sterile material or tailings will increase. Tailings are estimated to increase twice by 2035. According to Art. 23 D.S 148, 2003 (Sanitary Rules for Dangerous Waste Management), from the Ministry of Health, sterile material, low-grade ore, leaching wastes, tailings, and debris make up the so-called MMWs, which result from mining operations (Pérez et al. 2021). Tailings are deposited near mining sites. They can be defined as finely ground material piles consisting of a mixture of gangue, rock fragments, sediments, etc. Tailings are not originally considered "toxic"; however, they can acquire this characteristic when combined with water. Examples of this are arsenic, copper, zinc, lead, etc. (Adiansyah et al. 2015; Peña-Ortega et al. 2019).
On a country's basis, four technological challenges are defined: facing increasing water and surface scarcity, minimizing infiltration impact and ensuring ore deposit stability; promoting the change of wastes into assets; and fostering community inclusion and agreement. By facing these challenges, new mining is expected to not only be concerned about economic benefits from mineral production and exploitation but also committed to incorporating these sustainability elements in their processes and become an industry more friendly with the environment and the different habitats sharing the territory intervened.
In this new view of mining processes, another great concern is the responsible management of materials with low economic value, which are not of great interest for...
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