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Incremental, transitional and transformational adaptation to climate change in resource extraction regions

Published online by Cambridge University Press:  23 September 2019

Julia Loginova
Affiliation:
School of Earth and Environmental Sciences, The University of Queensland, St Lucia, QLD 4072, Australia
Simon P.J. Batterbury*
Affiliation:
School of Geography, The University of Melbourne, Parkville, VIC 3010, Australia Lancaster Environment Centre, Lancaster University, Lancaster, LA1 4YQ, UK
*
Author for correspondence: Dr Simon P.J. Batterbury, E-mail: simonpjb@unimelb.edu.au

Non-technical summary

Mining regions are affected by climate change. Supplies of energy and water are required, and operations become hazardous during adverse weather events. Adapting to climate change takes three forms: incrementally improving the resilience of mining operations; transitioning to more inclusive governance through institutional and policy innovations; and more profound transformations that shift the balance of power, including profit-sharing, localized control or cessation of mining entirely. Clarifying adaptation pathways helps to identify priorities and inform policies for a fairer and more sustainable future for mining and the regions where it takes place.

Type
Review Article
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted re-use, distribution, and reproduction in any medium, provided the original work is properly cited.
Copyright
Copyright © The Author(s) 2019

Social media summary

There are various adaptation pathways for mining regions to meet threats and opportunities presented by climate change.

1. Introduction

Regions that host the extraction of hydrocarbons, metals and minerals (referred to henceforth as miningFootnote 1) are strategically important in the response to anthropogenic climate change. Global advances in governance and growing awareness of climate change and its impacts are leading the mining industry, governments, civil society and other actors to make choices about technological, managerial and policy solutions that often clash with the continued demand for minerals and hydrocarbons (Odell et al., Reference Odell, Bebbington and Frey2018). ‘Adaptation’, ‘mitigation’, ‘resilience’ and ‘transitions’ have gained prominence in policy, planning, research and social protest about mining, particularly following the warnings issued by the Intergovernmental Panel on Climate Change (IPCC) and the United Nations Framework Convention on Climate Change (UNFCCC), and sustained by the burgeoning literature on the topic.

From a normative perspective, better climate change responses in mining regions offer some hope of more sustainable development in a climate-resilient future (Addison, Reference Addison2018; Ali et al., Reference Ali, Giurco, Arndt, Nickless, Brown, Demetriades and Yakovleva2017; Giurco & Cooper, Reference Giurco and Cooper2012; Hodgkinson & Smith, Reference Hodgkinson and Smith2018; Segura-Salazar & Tavares, Reference Segura-Salazar and Tavares2018). Viewed more critically, mining regions face the twin challenges of sustainability and justice. Issues include the ‘resource curse’ (Auty, Reference Auty2002), pollution (O'Rourke & Connolly, Reference O'Rourke and Connolly2003), conflicts over access to natural resources (Bebbington & Bury, Reference Bebbington and Bury2013; Hilson, Reference Hilson2002) and the alienation of local communities (Kemp et al., Reference Kemp, Owen, Gotzmann and Bond2011). Climate change has the potential to further aggravate existing social, environmental and economic vulnerabilities in mining regions (Phillips, Reference Phillips2016). Given these circumstances, one should be attentive to the extent that climate change responses can alter the complexities of regions where resource extraction is prioritized over other land uses. A key question is whether climate-resilient mining can exist at all, and in what form, in a nexus of communities, ecosystems and economies. A critical understanding of past and current initiatives is essential if maladaptation is to be avoided (Magnan et al., Reference Magnan, Schipper, Burkett, Bharwani, Burton, Eriksen and Ziervogel2016).

The goal of this article is to provide a comprehensive review of climate change responses in mining regions for research to adequately inform policy and planning and so that vulnerabilities can be addressed in present and future mining regions. Asking what adaptation is for enables us to identify priorities for action and to locate some overlooked dimensions. This work is built on and extends academic literature that only begins to establish an understanding of the complex relationships between climate change and resource extraction (Odell et al., Reference Odell, Bebbington and Frey2018; Phillips, Reference Phillips2016).

We systematically review and evaluate the scholarly literature that conceptualizes adaptation to climate change in mining regions and reports evidence of existing responses. We employ a framework of adaptation pathways developed by Pelling (Reference Pelling2011) that distinguishes between incremental, transitional and transformational adaptation. In this framework, adaptation refers to changes in practices in response to a changing environment (Pelling, Reference Pelling2011). After introducing the conceptual framework, we present evidence of emerging public and private initiatives based on available documentation against the framework and explain the methodology for the review. We then provide a synthesis of current knowledge by identifying major research themes that focus on incremental, transitional and transformational adaptation in mining regions, and we conclude by identifying key knowledge gaps, future research needs and opportunities for social learning. We hope the audience will be planners, the development sector, the mining industry, host communities, activists and scholars interested in adaptation to climate change and the challenges of sustainability and justice raised by mining in a changing climate.

2. A conceptual framework

Adaptation has been a central concept in several disciplines in the environmental and social sciences (Hoffmann & Sgro, Reference Hoffmann and Sgro2011; Smit & Wandel, Reference Smit and Wandel2006). It was first driven by evolutionary ideas and became a means for reflecting upon the link between society and the environment in a reciprocal way across scientific fields. Recently, the field of adaptation to climate change has gained prominence because of the acceleration of global environmental changes, an increased awareness about them and growing demands for adequate responses (Füssel, Reference Füssel2007).

Recent studies argue that contemporary challenges require approaches that integrate adaptation, mitigation and development (Naess et al., Reference Naess, Newell, Newsham, Phillips, Quan and Tanner2015; Thornton & Comberti, Reference Thornton and Comberti2017) and recognize interlinkages with sustainability and justice (Leach et al., Reference Leach, Reyers, Bai, Brondizio, Cook, Díaz and Subramanian2018). Incremental adaptation to climate change is insufficient, and rather society-wide transformations that enable political economic change and more inclusive development are needed (Gillard et al., Reference Gillard, Gouldson, Paavola and Van Alstine2016; O'Brien, Reference O'Brien2012; Park et al., Reference Park, Marshall, Jakku, Dowd, Howden, Mendham and Fleming2012; Waddell et al., Reference Waddell, Waddock, Cornell, Dentoni, McLachlan and Meszoely2015). The framework of adaptation pathways proposed by Pelling (Reference Pelling2011) is one comprehensive way to distinguish climate change responses aimed at proximate causes of vulnerability from those seeking broader systemic change in social and political regimes. There are three adaptation pathways: incremental, transitional and transformational, each encompassing various goals, scopes and temporal and spatial scales (Table 1).

Table 1. Adaptation pathways (adapted from Pelling, Reference Pelling2011).

Incremental adaptation is orientated at resilience. The main goal is to secure continuation of desired systems into the future in the face of changing contexts and uncertainty (Pelling, Reference Pelling2011). Climate change impacts are seen as the major source of vulnerability. The proposed solutions are centred on technological and managerial fixes that are responsive to a particular event or have a preventative character. Transitional adaptation is reformist. It involves changes to social relations and behaviour within the prevailing order (Pelling, Reference Pelling2011). ‘Transitional’ ideas have been guided by substantively different approaches. ‘Sociotechnical transitions’ (e.g., Geels, Reference Geels2005) refer to a shift to a low-carbon development as an attempt to restructure the global fossil fuel-based economy through social innovations and technology. A ‘sustainability transition’ is required to adapt societies and economies to sustainable production and consumption (e.g., Raskin et al., Reference Raskin, Banuri, Gallopin, Gutman, Hammond, Kates and Swart2002). ‘Just transition’ improves equity and considers impacts for different social groups (e.g., Evans & Phelan, Reference Evans and Phelan2016). Transitional adaptation places vulnerabilities related to climate change alongside socioeconomic, political and environmental processes. The overall goal is adaptation in governance and institutions, including achieving institutional legitimacy, inclusion of previously excluded values and implementation of legal responsibilities.

The resilience- and transition-orientated approaches are criticized for downplaying the significance of real-world political processes and inequalities that shape relationships between society, environment and economy, and for their short-term technological and managerial optimism (Park et al., Reference Park, Marshall, Jakku, Dowd, Howden, Mendham and Fleming2012). Taking a more critical perspective, transformational adaptation harnesses opportunities that challenge the status quo of existing economic and social structures and values, shifting the balance of power further towards justice (Pelling, Reference Pelling2011). Orientated at the root causes of vulnerability, it requires a regime change from the level of individual behaviour through to the structures of the global political economy.

This typology of adaptation pathways identifies social, cultural and political economic processes through which adaptation responses unfold. Moreover, it has value in placing adaptation pathways within the broader context of human development, justice and sustainability. Therefore, it is useful for understanding the reciprocal relations between environment and society in complex, contested and dynamic regions where mining takes place. Before explaining the methodology, we provide evidence of past and current industry, public policy and societal initiatives and characterize them using this conceptual framework.

3. Emerging responses to climate change in mining regions

Global climate change and earth system governance initiatives establish a framework for mining regions to address the threats and opportunities provided by climate change. International policy promotes strategic climate actions: mitigation and adaptation were set as two global responses by Article 4 of the UNFCCC (1992). In the fifth IPCC report, mitigation refers to interventions to reduce the sources or enhance the sinks of greenhouse gases and adaptation is defined as the process of adjustment to existing or expected climate change and its impacts (2014). The 2015 Paris Agreement for Climate Action sets mitigation goals to limit dangerous global warming to less than 2°C compared to preindustrial levels (UNFCCC, 2015).

There are global and regional scientific predictions – still uncertain – that the mining sector in the future will have to contend with different climatic conditions, with adverse impacts on industrial operations, regional economies, communities and ecosystems (IPCC, Reference Field, Barros, Dokken, Mach, Mastrandrea, Bilir and White2014). Climate change will likely alter access to water and increase risks to infrastructure, particularly in regions with higher water stress where many mines are located (Northey et al., Reference Northey, Mudd, Werner, Jowitt, Haque, Yellishetty and Weng2017). With poorer-grade mineral deposits, less favourable environments and more unconventional methods of extraction (e.g., coal seam gas), the extra demand for energy and water will also increase the sector's footprint. In addition, extreme climatic conditions are predicted to intensify in regularity and severity (IPCC, Reference Field, Barros, Dokken, Mach, Mastrandrea, Bilir and White2014).

New governance arrangements and the shifting risks at mine sites have led to a range of initiatives in industry practice, public policy and social protest across geographical regions. We now describe emerging responses to climate change found in mining regions and consider them against our conceptual framework of adaptation pathways. We find that private and public initiatives correspond largely to incremental and transitional adaptation, while societal responses urge transformations.

3.1. Industry initiatives

Companies have been increasingly taking an active role in climate actions as initiators, catalysts and participants in industry-led and multi-stakeholder efforts (Bach, Reference Bach2019). They have been supporting emissions reductions (Kolk & Levy, Reference Kolk and Levy2001), not least by engaging in the UN Climate Change Conferences (Slezak, Reference Slezak2016). Some corporations have reconsidered their business models to include innovative solutions to offset their climate impacts (e.g., through renewable energy) and to enhance their sustainability performance (Bach, Reference Bach2019; Tost et al., Reference Tost, Hitch, Chandurkar, Moser and Feiel2018).

Incremental adaptation has received prominence in the private sector's agenda (Averchenkova et al., Reference Averchenkova, Crick, Kocornik-Mina, Leck and Surminski2016). The Global Oil and Gas Industry Association for Environmental and Social Issues (IPIECA), the International Council on Mining and Metals (ICMM) and the Business for Social Responsibility network (BSR) have developed guidelines in a suite of documents that assist companies in identifying climate change risks, preparing adaptive responses and developing climate-related sustainability reports (BSR, 2011; ICMM, 2011, 2013; IPIECA, 2013, 2016). Additionally, the 2030 Agenda for Sustainable Development and the Sustainable Development Goals established a pro-climate action focus (Goal 13) (UNSDSN, 2015). The interinstitutional White Paper “Mapping Mining to the Sustainable Development Goals” interprets Sustainable Development Goal 13 to include building climate change resilience and recognizing climate change in planning and investment in mines (WEF, 2016, p. 54).

The BSR (2011) recommends that mining companies seize the opportunity presented by climate change to collaborate with communities, governments, non-governmental organizations and development agencies in addressing climate change. The La Granja project was commissioned by the ICMM for Rio Tinto in Peru to find ways to enhance the capacity of copper mining host communities to adapt to climate change (ICMM, 2014). Another example is the Declaration on Resource Development Principles in Inuit Nunaat (parts of northern Canada, Russia, Greenland and Alaska in the USA). According to this document, resource development in the Inuit territory can only take place if it contributes to “global, national and regional efforts to curb greenhouse gas emissions and should always be seen through the reality of climate change” (ICC, 2011, art. 5). These initiatives engage different stakeholders in dialogue over climate change challenges and indicate transitional pathways to adaptation.

3.2. Public initiatives

Public responses are primarily orientated at transitional adaptation that includes experimentation with governance. For example, the assessment of environmental impacts required for the planning of new or expanding of existing mine sites can address actual and anticipated climate change risks (Agrawala et al., Reference Agrawala, Matus Kramer, Prudent-Richard, Sainsbury and Schreitter2012). Regulatory agencies in a range of countries (Canada, the USA, Chile and the European Union) as well as international institutions (the International Finance Corporation and the World Bank) have formalized this need (Capstick et al., Reference Capstick, Kelly, Barrett and Penailillo2014).

Another example of governance innovation is designating no-go areas for mining that have implications for climate change adaptation. Restrictions on open pits have been applied in Costa Rica and in some provinces of Argentina and the Philippines (Gera, Reference Gera and Mauerhofer2016). Belize, Costa Rica, France and New Zealand have placed constraints on offshore oil prospecting and extraction. Limiting fossil fuel supply is necessary to achieving the goals set by international climate policy: studies show that many of the world's reserves of oil (a third), gas (half) and coal (80%) should remain underground from 2010 to 2050 (McGlade & Ekins, Reference McGlade and Ekins2015).

Governments of other countries continue granting licenses and providing subsidies to the mining and oil industries (e.g., Australia, Norway and Russia). Fossil fuel-rich countries experience the greatest exposure in the climate-constrained world, and they are advised to facilitate exploration and to accelerate development of existing deposits in order to benefit from the oil sector, at least in the short term (Manley et al., Reference Manley, Cust and Cecchinato2016), while prospecting for other sources of revenues, as Saudi Arabia has begun to do.

Governments in regions that are vulnerable to the impacts of climate change have confronted the global mining industry, holding major polluters accountable for their impacts. The government in Kiribati proposed a global moratorium on coal mining expansion to save low-lying islands from rising seas (PIDF, 2015). The governments of the Philippines initiated a legal human rights case targeting fossil fuel companies that are among the major greenhouse gas emitters (Vidal, Reference Vidal2016).

Experiments in climate and resource governance are not limited by national boundaries, but are implicated in multiple forms of governance at various scales. They can clash with the complex realities of global markets, international institutions and geopolitics, causing a misfit of emerging initiatives with existing global policy. One example was an initiative proposed by the former President of Ecuador, Rafael Correa, to suspend oil extraction in the Ishpingo-Tambococha-Tiputini part of the Yasuni National Park (the Yasuni-ITT Initiative). This initiative failed because decision-makers could not resolve tensions between socio-political relations in Ecuador, the need for oil revenues, the inflexibility of international environmental governance and commitments to compensate Ecuador for lost oil revenues (Pellegrini et al., Reference Pellegrini, Arsel, Falconí and Muradian2014).

3.3. Societal initiatives

Societal pressure for mining regions to address climate change includes an emerging wave of climate activism throughout the world. The lack of adequate political action on the issue has resulted in social and environmental movements that demand constrains on fossil fuel supply through pipeline protests, fossil fuel divestment proposals and anti-fracking campaigns (Piggot, Reference Piggot2018). Legal activism is a part of the movement. In 2016–2017, environmentalists initiated a lawsuit against the Norwegian government's plans for offshore oil extraction in the Arctic (SaveTheArctic, 2017). In Alaska, there have been legal claims to the energy sector for contributing to the loss of the island of Kivalina, where the Native Village of Kivalina is located, because of rising sea levels (Abate, Reference Abate2013).

More radical perspectives include societal demands for systemic transformations to decreased material consumption, de-growth, alternative development and post-extractivist futures. Mining is no exception, and Bendell (Reference Bendell2018) argues that the reformist approach to sustainable development, resilience and corporate sustainability is now redundant when faced with the cruel reality shown by the climate change data. His deep adaptation agenda calls for radical societal changes and facing up to impending doom (Bendell, Reference Bendell2018).

As new private and public actions emerge, incremental rather than deep transformational adaptation still guides the industry sector. Actions maintain a prevailing logic that extraction is inevitable but should be performed in a more sustainable manner to ensure the legitimacy and social acceptance of mining operations. Transitional ideas of restricting mining on climate grounds are very rare, usually where ecosystems and livelihoods are extremely vulnerable to the impacts of climate change or where resource deposits are small. Societal responses urge for transformational adaptation, demanding climate justice and control over development and the future. After defining a methodology for the review of the literature, we characterize current conceptualizations of adaptation in mining regions in selected literature.

4. The review approach

Our systematic review follows guidelines suggested by Petticrew and Roberts (Reference Petticrew and Roberts2008). This approach enables us to evaluate existing knowledge while identifying gaps and directions for future research. The review strategy required us to explicitly identify inclusion and exclusion criteria. Articles were found in the Web of Science using the following combinations of words: (“mining” OR “resource extraction” OR “mineral” OR “oil”) AND (“climat* chang*” OR “global warming”) AND (“adapt*”) with no date restrictions. The search in May 2019 yielded a total of 672 results.

Since our interest lies in adaptation as a conceptual category, we targeted scholarly journals and excluded other sources, but acknowledge that relevant material is also published in books (e.g., Carlson et al., Reference Carlson, Goldman, Dahl, Drake, Kontar, Eichelberger, Rupp and Taylor2016; Newton et al., Reference Newton, Paci, Ogden and Haque2005; Sharma, Reference Sharma, O'Callaghan and Graetz2017; Taylor, Reference Taylor2015) and as reports, such as in Canada (e.g., Duerden et al., Reference Duerden, Pearce, Ford and Pittman2014; Pearce et al., Reference Pearce, Ford, Prno and Duerden2009) and Australia (e.g., Hodgkinson et al., Reference Hodgkinson, Littleboy, Howden, Moffat and Loechel2010; Maru et al., Reference Maru, Chewings and Sparrow2012; Mason & Giurco, Reference Mason and Giurco2013). We also concentrated our review on sources in English, excluding studies published in Spanish (e.g., Navarro, Reference Navarro2017; Seoane et al., Reference Seoane, Taddei, Algranati and Borón2013), French (e.g. Damian, Reference Damian2014) and other languages. We excluded articles whose focus, according to the Web of Science categories, did not fit in the field of social sciences (we included interdisciplinary studies). As a result, 88 articles were selected as potentially relevant.

The title, keywords and abstract of each article were screened independently by two reviewers (JL, SPJB) and articles were included only if they addressed matters relevant to this review. For example, studies that addressed logging as a resource extraction activity were excluded. The lists of references were considered and compared to the preliminary selection. If not identified through our initial search, additional articles were included. At the end, 44 academic peer-reviewed articles in English were included in this systematic review.

We read each contribution and identified four aspects that characterize adaptation pathways (according to Table 1): goal, scope, time and scale. Based on these aspects, we classified the articles into three groups corresponding to types of adaptation pathways (incremental, transitional and transformational). If more than one was represented, only the most important pathway was identified. Disagreements of interpretation were resolved by discussion between the authors.

We used latent content analysis of the selected articles to identify key themes underlying the conceptualization of adaptation actions. This involved in-depth reading of all of the publications and interpretation of contextual information against the conceptual framework. In the following section, we synthesize the information and identify the dominant debates, shortcomings and learning opportunities.

5. The current state of research on adaptation in mining regions

The concept of adaptation to climate change has been increasingly applied to the mining context. With few articles published on the topic in the 2000s, the annual number of articles since the year 2010 has been between two and eight (Figure 1). Among the 44 articles included in this analysis, 16 articles focus on incremental adaptation, 15 report transitional adaptation and 13 address transformational adaptation. Some 18 countries and 4 major regions (the Arctic, the Amazon, Africa and small islands in Oceania) were covered, with a third of the studies having a defined geographical area conducted in Australia (8) and Canada (6). In approximately half of the studies, the authors reported the results of original studies that drew on qualitative and mixed-method research.

Fig. 1. Selected articles representative of Pelling's typology of adaptation pathways, year of publication and geographical coverage. Each line represents an individual article colour-coded depending on the classification into one of the three adaptation pathways. N/S = non-specified.

5.1. Incremental adaptation

The incremental adaptation pathway prevails in the assessments of vulnerability of the mining industry to climate change, its adaptive capacity and adaptation strategies in Canada and Australia. Based on surveys of mining representatives in Canada at a senior corporate (Ford et al., Reference Ford, Pearce, Prno, Duerden, Berrang Ford, Beaumier and Smith2010) and mine site level (Ford et al., Reference Ford, Pearce, Prno, Duerden, Ford, Smith and Beaumier2011), studies showed that a majority of informants perceived that their companies were taking engineering and administrative actions to manage the impacts of climate change. The uncertainty of climate projections and regulatory regimes and the cost of adaptation were recognized as the main barriers to action. Pearce and collaborators (Reference Pearce, Ford, Prno, Duerden, Pittman, Beaumier and Smit2011) conducted in-depth interviews with mining professionals in Canada and found that limited adaptation planning for future climate change was underway. Diamond-mining companies in the Northwest Territories, for example, have explored alternative means of transportation and routes to adapt to warmer winter temperatures and the vulnerability of the ice road network. The adaptation strategy of sodium sulfate mines in Saskatchewan has included diverting rivers and building dikes and water storage areas in response to increased fluctuations in water supply and seasonal precipitation.

In Australia, Hodgkinson et al. (Reference Hodgkinson, Hobday and Pinkard2014) synthesized findings from a range of case studies, regional workshops and surveys of over 200 mining companies. They concluded that adaptation in the mining sector in Australia was driven by “too much or too little water,” with implications for access to water for processing and dust handling, interruptions to operations and flooding of pits. Adaptation strategies were related to integrated risk management, treatment and storage of groundwater, local drainage systems, advanced treatment of wastewaters and long-term forecasting for preparation for floods and storms. Another study found that adaptation activities in Australia were actually more important for local government authorities than for mining companies (Loechel et al., Reference Loechel, Hodgkinson and Moffat2013). The authors suggested that mining companies had fewer concerns about future impacts as they discounted the risks due to a degree of climate change scepticism.

Pizarro and others (Reference Pizarro, Sainsbury, Hodgkinson and Loechel2017) documented the impacts of climate change on the Australian uranium industry (the Ranger and Olympic Dam mines) and found that tailing and waste storage facilities, ore extraction and transportation were the main operational disruptions, increasing costs and losing revenue. They concluded that while short-term adaptation was underway, no long-term planning to face climate risks was in place. It was suggested that the adaptive capacity of the industry could be enhanced by improving operational and management procedures, particularly communication with related companies in the supply chain.

Nunfam et al. (Reference Nunfam, Oosthuizen, Adusei-Asante, Van Etten and Frimpong2019) studied mining workers’ adaptation strategies to heat-exposure risks in Ghana. They demonstrated that the extent of concerns about workplace heat exposure differed significantly between small-scale and large-scale mining, and so did adaptation strategies of workers who had varying access to adequate water intake, work-break hours, shade, light clothing and cooling systems (Nunfam et al., Reference Nunfam, Van Etten, Oosthuizen, Adusei-Asante and Frimpong2019). Therefore, climate change adaptation intervention and planning should include a concerted effort among stakeholders to include observed disparities in mining activity (Nunfam et al., Reference Nunfam, Van Etten, Oosthuizen, Adusei-Asante and Frimpong2019).

In situ climate change adaptation planning in mining regions requires responsive regulations and planning frameworks. Sharma and Franks (Reference Sharma and Franks2013) studied the experience of responses to extreme flooding in Queensland in Australia in 2007–2008 and 2010–2011. In this case, inflexible regulatory requirements to restrict water discharge from mine sites resulted in mines being flooded during these extreme weather events. In another case, Carkovic and collaborators (Reference Carkovic, Calcagni, Vega, Coquery, Moya, Bonilla and Pastén2016) urged for enhanced planning and flexible solutions in regions with abandoned mines and tailings where the risks from the exposure to climate-related events are particularly high. Knowledge-based and cost-effective strategies are needed to deal with abandoned tailings in northern Chile, a dryland region with extensive copper and iron-ore mining activities. Information and communication technology can assist in the environmental simulation and modelling that enables localized responses and adaptation. For example, just-in-time alert warning and digital electronic platforms for information sharing were employed as part of risk reduction in South Africa's mines (Aleke & Nhamo, Reference Aleke and Nhamo2016).

Incremental adaptation strategies address the implications of climate change for the economic performance of the mining sector. Prowse and his collaborators (Reference Prowse, Furgal, Chouinard, Melling, Milburn and Smith2009) reviewed the economic risks and opportunities for mining threatened by the impacts of climate change in Canada and argued that technological adjustments were needed to ensure economic stability and growth in the sector. Damigos (Reference Damigos2012) quantified the economic losses from climate change for the Greek mining industry without adaptation at more than US$0.8 billion, proposing that the cost of effective adaptation would be limited to US$312 million.

Kolk and Levy (Reference Kolk and Levy2001) in their study of early shifts in corporate climate strategies among oil multinationals identified factors that explain the development of climate policies: locational (e.g., regulatory policies, culture and societal concerns) and internal company-specific factors (e.g., degree of centralization and the presence of climate scientists among the staff). However, it was the market position and economic competition that affected the uptake of climate actions the most. Martus (Reference Martus2019) found significant variations within climate strategies employed by metals mining companies in Russia, with some firms being proactive and others reluctant. The author attributed these differences to the disproportionate effects of international and national policies on corporate strategies, as well as their varying reputational concerns.

Only one study in this group was concerned with the human–environment interactions in mining regions. Evans (Reference Evans2008) studied coal-mining communities in the Hunter Valley in Australia and argued that an essential condition for climate change adaptation in this region is action to remediate decades of open-cut coal mining, which has disrupted regional socio-ecological systems (and continues to do so).

5.2. Transitional adaptation

The framing of adaptation as transitional is employed in studies that suggest new approaches orientated at sustainable and climate-compatible development (CCD) in mining regions. Jegede (Reference Jegede2016) argued that climate change adaptation could motivate sustainable mining and the green economy across African countries, for example, through the development of alternative sources of energy to use for mining and the reforestation of regions to rehabilitate abandoned mine sites. More broadly, successful co-adaptation–mitigation responses will contribute to the sustainability of mining (Hodgkinson & Smith, Reference Hodgkinson and Smith2018). Similar observations were made earlier by Irarrázabal (Reference Irarrázabal2006), who argued that climate change strategies are implicated in the industry's voluntary actions, particularly corporate social responsibility.

Three articles addressed the integration of the challenges and opportunities presented by climate change adaptation into the industry's voluntary actions and development efforts through CCD, defined as “development that aims to minimize the harm caused by climate impacts, while maximizing human development opportunities presented by a low emissions, more resilient future” (Dyer et al., Reference Dyer, Leventon, Stringer, Dougill, Syampungani, Nshimbi and Kafwifwi2013, p. 2). Leventon et al. (Reference Leventon, Dyer and Van Alstine2015) studied the role of mining in CCD in Zambia and found that mining companies operating locally have been increasingly designing corporate social responsibility strategies to align with the need to support the livelihoods of host communities affected by climate change. This can be best achieved through partnerships, where mining companies typically provide financial resources and communities offer local expertise and labour (Dyer et al., Reference Dyer, Leventon, Stringer, Dougill, Syampungani, Nshimbi and Kafwifwi2013). Based on a range of case studies in Oceania (phosphate mining in Nauru and Kiribati, oil and gas mining in Timor-Leste and coal mining in West Papua and Papua New Guinea), Bambrick (Reference Bambrick2018) emphasized the importance of CCD that is health promoting and excludes resource extraction if the resilience of small-island communities is to be built.

Transitions require institutional innovations across various scales of resource and climate change governance. At the global scale, new institutional arrangements are vital to ensuring that growing demand for the minerals needed for low-carbon development does not come at the expense of environmental sustainability in places of their extraction (Ali et al., Reference Ali, Giurco, Arndt, Nickless, Brown, Demetriades and Yakovleva2017). Actions are necessary along the mining value chain and must include monitoring of mineral production and consumption, coordination of mineral exploration between countries, investments in new extraction technologies, promotion of best practices and development of inventories for recyclable metals (Ali et al., Reference Ali, Giurco, Arndt, Nickless, Brown, Demetriades and Yakovleva2017).

At the local scale, institutional innovations are essential to promoting greater dialogue between host communities, governments and mining companies. Eisenstadt and West (Reference Eisenstadt and West2016), in a study of perceptions and beliefs about climate change among Indigenous peoples in Ecuador, found that communities affected by oil drilling (Kichwa and Waorani peoples in Napo province) consider the ‘climate change’ narrative as a means to advocate against state and oil companies for their needs and rights. The authors also suggest that “indigenous people may be strong natural allies in climate change mitigation and adaptation” (Eisenstadt & West, Reference Eisenstadt and West2016, p. 55), but that a dialogue has been lacking, limiting the potential of climate change adaptation to achieve sustainable outcomes. In Australia, Birch (Reference Birch2016) stressed the importance of engaging Aboriginal communities affected by mining in efforts to support climate-resilient development in an ethical and egalitarian way, based on greater recognition of traditional knowledge systems and acknowledging previous destructive impacts on their livelihoods and cultural values. The most commonly mentioned adaptation strategy for the Yolngu Aboriginal people in Arnhem Land was to establish culturally appropriate communication channels and practices that guarantee their inclusion into the management of mining and climate change impacts, recognize the Yolngu language and traditional institutions and ensure transparency and honesty in decision-making (Petheram et al., Reference Petheram, Zander, Campbell, High and Stacey2010).

Climate change actions by the private sector might be increasingly required for maintaining the legitimacy of mining and gaining the social license to operate (the ongoing acceptance of a company's practices). Odell et al. explain that, for the mining industry in Chile, “climate-change related pressures on water and energy resources demand that the sector goes through ‘a socio-technical regime change’, not only as an adaptive response, but also because in a context of climate change, ‘the forms of gaining legitimacy have changed’” (Odell et al., Reference Odell, Bebbington and Frey2018, p. 209). Pellegrino and Lodhia (Reference Pellegrino and Lodhia2012) argued that environmental and climate disclosure by the mining industry in Australia via different media has been increasingly critical for achieving the social acceptance of mining.

The idea that our society should limit the extraction and use of fossil fuel reserves to prevent dangerous climate change (McGlade & Ekins, Reference McGlade and Ekins2015) has generated a debate on whether and under which conditions extraction should proceed. Bos and Gupta (Reference Bos and Gupta2016) argued that right-to-development and equity principles should be used in planning decisions for future oil projects in the Global South. They suggest that new oil projects in Kenya should proceed because citizens of the country largely support oil extraction. This argument has also been made to support the capture of revenues from oil and gas extraction in South-East Asia's poorest nation, East Timor.

Studies also reported challenges to transitions in industrial and post-industrial countries. Evans (Reference Evans2007) examined the potential for a just transition in the Hunter Valley, a major coal-mining region in Australia. The author found that government sustainable interventions were lacking, and it was collective action by key labour unions, environmentalists and local residents that harnessed transitional adaptation pathways. In Canada, unprecedented fires affected oil sands-producing regions in Fort MacMurray, Alberta, in 2016. The immediate response to the disruptions was to restart oil production immediately, without questioning the implications of or for climate change. Patterson and others (Reference Patterson, Thaler, Hoffmann, Hughes, Oels, Chu and Jordan2018) explained that the dominant logic of resilience-orientated adaptation and a ‘jobs versus environment’ discourse had prevented consideration of ending climate-damaging activities in this vulnerable region. Instead, a dialogue with oil-industry workers and civil society organizations was needed to enable alternative pathways, such as by providing support to skilled employees to transit to work in the renewable energy industry.

5.3. Transformational adaptation

The transformational adaptation pathway stresses the adverse fallouts from political economic structures in mining regions in which development and power are highly unequal and justice is poorly served. A representative article by Cameron (Reference Cameron2012) critiqued the climate change adaptation research that became dominant in how adaptation is framed and addressed in northern Canada. The author argued that this literature systematically overlooks the legacy of colonialism and the profound significance of resource development in the Arctic. This omission, the author states, “contributes to a broader delimitation of Inuit political interventions into … resource development, and climatic change” (Cameron, Reference Cameron2012, p. 105).

Other contributions emphasize the risks of neglecting the heterogeneity of local representation and traditional institutions, which threatens equitable climate change responses and can potentially exacerbate vulnerabilities and conflicts. Company strategies to manage carbon emissions from land-use changes, promoted by global climate change governance (e.g., REDD+, which stands for Reducing Emissions from Deforestation and Degradation), reflect an increasingly neoliberal approach to climate change actions through the commodification of carbon and payments for ecosystem services (Hirons et al., Reference Hirons, Hilson, Asase and Hodson2014). The study examined the potential of forestry to provide benefits from carbon sequestration for mining companies in Ghana, and the results suggested that these initiatives marginalized the concerns and interests of local communities and aggravated existing inequitable benefit-sharing practices through local elite capture and by alienating communities from the land (Hirons et al., Reference Hirons, Hilson, Asase and Hodson2014).

Curley (Reference Curley2018) studied the potential of the Green Jobs initiative of the Navajo Nation in the USA to help transition from coal dependency towards renewable energy projects. The initiative largely failed because of the complexities of the Nation's traditional governing structures and the weak legitimacy of new arrangements among community members because of its perceived neoliberal approach. Greenland is another place where traditional indigenous institutions meet the neoliberal mining agenda. However, considering relatively well-developed Greenlandic sovereignty and institutions, the outcomes are likely to be inclusive of the priorities of the Greenlandic Inuit (Nuttall, Reference Nuttall2012). Adaptation in mining contexts where extractive culture and traditional institutions clash will never be optimal, especially when viewed against more radical options – progressive profit-sharing, cessation of mining or localized control (as, for example, in one case of majority Indigenous shareholding in nickel mining in New Caledonia).

An essential attribute of transformational adaptation is whether local communities are active in taking control over an uncertain future in the face of resource extraction activity and climate change. Peasant farmers and herders in the Peruvian Camaná-Majes-Colca watershed have engaged in creative political actions, such as claiming water rights and demanding payments from the mining companies using the water (Stensrud, Reference Stensrud2016). The role of ‘social regulation’ is also evident in Kronenberg's (Reference Kronenberg2013) study of open-pit mining under glaciers. The author demonstrated how the impacts of gold mining on glacier destruction elicited the social and symbolic values attached to the glaciers, helping to protect them in Argentina and Chile (with empowered societal and institutional settings), but not in Kyrgyzstan (with weak institutions and rules) (Kronenberg, Reference Kronenberg2013).

In remote regions where Indigenous and non-Indigenous people maintain subsistence lifestyles and traditional institutions are far from centres of political power and are not adapted to modern solutions, local control of mining is rare. Mining corporations, governments and development agencies have far greater power over development and land use. As a result, the extensive and poorly controlled development of mining combined with the impacts of climate change have resulted in a low chance of finding good-quality pastures for reindeer herds in Subarctic and Arctic climates (Kuemmerle et al., Reference Kuemmerle, Baskin, Leitão, Prishchepov, Thonicke and Radeloff2014) and herds in Oman (Sternberg & Chatty, Reference Sternberg and Chatty2016), for example. The voices of the herders have been marginal in regional and national political discourses about mining. While mining has expanded, the adaptive capacity of herders has suffered.

It is challenging to implement climate change initiatives in regions where mining is dominant politically. In a discussion of governance challenges in the face of climate risks in El Salvador (a country that has recently rejected large-scale mining), Bebbington and his collaborators (Reference Bebbington, Bury, Cuba and Rogan2015) exposed conflicts over government mandates, particularly between economic and environmental ministries, difficulties in managing conflicts over mining leases and social development and higher-order processes governing transnationals and their actions across scales. In their view, all of these need to be resolved in El Salvador before the commencement of large-scale mining if resilience in the face of climate change risks is a concern.

Piggot (Reference Piggot2018) argued that social movements can shift the political landscape towards restricting fossil fuel extraction. However, challenged by the ‘social license to operate’ in a changing climate, the mining industry can employ a range of legitimizing and repressive strategies in order to maintain mining. For example, as resistance to coal has grown in Germany, mining has been made to look ‘sustainable’ (Brock & Dunlap, Reference Brock and Dunlap2018). Moreover, mine-operating companies have employed political lobbying and overtly repressive techniques to continue operations of the Hambach open-pit coal mine, one of the world's largest (Brock & Dunlap, Reference Brock and Dunlap2018).

Society-wide solutions are needed not only to lower the demand for unsustainable sources of energy, but also to contribute to the mitigation of the impacts of resource extraction locally and regionally (Martinez-Alier & Temper, Reference Martinez-Alier and Temper2007). Orta-Martínez and Finer, in concluding their study of Achuar peoples’ resistance methods to oil extraction in the Amazon, suggest that “other alternatives should be considered when defining the development strategy such as securing human rights, stability and peace in the whole region, helping to avoid climate change, and preserving unparalleled biodiversity at world level” (Reference Orta-Martínez and Finer2010, p. 216).

6. Discussion: adaptation pathways in mining regions

The way adaptation to climate change is framed informs policy and practice with potentially profound and far-reaching implications for the future (Newman & Park, Reference Newman and Park2003; Park et al., Reference Park, Marshall, Jakku, Dowd, Howden, Mendham and Fleming2012). This review emphasizes that adaptation in mining regions can take different pathways, each with a specific goal and scope of interventions and varied temporal and spatial scales. A single concept cannot do justice to the diversity of challenges in mining regions. Drawing on the evidence summarized in the previous sections, we characterize each adaptation pathway in mining regions in Table 2.

Table 2. Adaptation pathways in mining regions.

Incremental adaptation in mining regions entails maintaining mining in place and protecting industrial infrastructure and employees while mitigating environmental disasters at mine sites. The prevalent academic debates concentrate on the following themes: assessments of vulnerability, adaptive capacity and adaptation by and for the mining industry (e.g., Ford et al., Reference Ford, Pearce, Prno, Duerden, Ford, Smith and Beaumier2011; Loechel et al., Reference Loechel, Hodgkinson and Moffat2013); in situ adaptation planning and adaptive regulations (e.g., Sharma & Franks, Reference Sharma and Franks2013); offering an economic and political rationale for adaptation (e.g., Damigos, Reference Damigos2012); and strengthening resilience of mining regions as socio-ecological systems (e.g., Evans, Reference Evans2008). Adaptation initiatives are reactive, providing reputational and economic benefits for mining companies. Positive outcomes include improved existing mining technologies and managerial practices that potentially lower the risk of serious accidents. Despite such efforts, incremental adaptation can allow mining companies to continue unsustainable and socially unjust operations that best serve established values. Opportunities for learning include enabling adaptive regulations, integration of information and communication technologies, addressing the legacy of previous mining operations and a focus on preventative rather than purely reactive initiatives.

Transition-orientated adaptation in mining regions emphasizes the potential of climate responses to motivate more sustainable mining and a greener economy through voluntary corporate initiatives and innovations in governance across different scales. Inclusion of host communities and workers in decision-making about the future of resource extraction and their more equal participation in the implementation of any initiatives are vital to ensuring inclusive and informed adaptation with more equal outcomes (e.g., Birch, Reference Birch2016). Finally, studies address the legitimacy of mining projects (particularly coal and oil) within the existing climate change governance regime and the fairness of transitions away from resource extraction towards sectors that support renewable energy and better products (e.g., Bos & Gupta, Reference Bos and Gupta2016). Through CCD, mining companies and governments can support local livelihoods and promote the health of communities adapting to the impacts of climate change (e.g., Dyer et al., Reference Dyer, Leventon, Stringer, Dougill, Syampungani, Nshimbi and Kafwifwi2013; Leventon et al., Reference Leventon, Dyer and Van Alstine2015). The main opportunity for learning includes more inclusive decision-making. However, the mechanisms of inclusion of local values and traditional institutions in adaptation planning in mining regions are likely to vary from region to region, requiring context- and culture-specific approaches.

Transformation-orientated studies challenge solutions aimed at maintaining the function of mining, framing mining as dangerous to people and the planet, with hazardous working environments, the displacement of local people, sustaining inequalities and poverty and further contributing to climate change. In addition, the political ecology and economy of mining regions include their colonial history, large commercial profits – sometimes shared with governments – and serious land-use conflicts (e.g., Cameron, Reference Cameron2012). For climate change responses to achieve sustainable and fair outcomes, development priorities other than mining must be considered, and growth-orientated and consumerist models that drive the demand for minerals and fossil fuels need to be rethought (e.g., Martinez-Alier & Temper, Reference Martinez-Alier and Temper2007). Current environmental crises offer opportunities, aside from mining, for changing the ways of seeing, acting and engaging with the natural world (Bendell, Reference Bendell2018; Waddell et al., Reference Waddell, Waddock, Cornell, Dentoni, McLachlan and Meszoely2015).

While we have phrased incremental, transitional and transformational adaptation pathways targeted at mining regions as separate categories for the purposes of the review, they are intersecting and overlapping. Technical incremental efforts in fact mitigate damage to mining infrastructure as well as local communities. Transitional responses encourage new institutional arrangements for more inclusive decision-making and more efficient resource use. But we argue that the world needs to move towards transformational thinking, and the other two stages are essential but insufficient to meet the challenge of a changing climate. The overall agenda for concerned scholars, politicians, practitioners and citizens is reduction in demand for minerals and resources, particularly fossil fuels, and restricting their supply when justified. Yet mining is a necessary component to capitalist economic growth providing for a growing population. It is also essential to supplying the raw materials needed for new technologies to enable renewable energy transitions. Many economies depend on mining, providing employment and livelihoods. Therefore, emphasizing priorities at a single scale (national priorities for development) or of only a single actor (e.g., the mining industry) ignores and may obscure other perspectives, reinforcing unequal power relations.

Addressing multi-scale concerns requires a better understanding of the interplay between incremental, transitional and transformational adaptation pathways. Hadarits et al. (Reference Hadarits, Pittman, Corkal, Hill, Bruce and Howard2017) studied interdependencies among and across scales and actors in the context of adaptation pathways for Canadian agriculture and found various ways in which one type of adaptation can influence (constrain or reinforce) other types. For example, extreme events that are perceived to result in crisis situations may prompt transformation. An improved understanding of these interactions in mining regions may help identify the processes occurring within these regions that facilitate movement from one to the other.

A possible solution to handling adaptation by means of multiple pathways is to embrace ‘clumsy solutions’. These allow for the inclusion of many different viewpoints to address the uneasy coexistence of incompatible goals (Verweij et al., Reference Verweij, Douglas, Ellis, Engel, Hendriks, Lohmann and Thompson2006). Often, the interaction between companies, governments and local communities proves to be challenging, especially in contexts with a legacy of mining-induced conflicts. Emphasizing the coexistence of multiple viewpoints can enable renegotiation of practices based on reflection on how problems and desired outcomes are framed, by whom, with whom and at what scale, and it can contribute to finding better ways for mining regions and broader society to prepare for the future in a changing climate.

7. Conclusion

This article assembles the expanding research on adaptation to climate change in mining regions. In providing specific examples, the review emphasizes that initiatives under an ‘adaptation’ framing are many and may be substantially different. For example, studies prioritize various suggestions in relation to the status quo of mining in the changing climate. In providing an outline of some aspects of incremental, transitional and transformational adaptation pathways, we found a lack of conceptual clarity. The way that dominant narratives about adaptation have emerged in scholarly work and policy, especially through private initiatives, has led to a mine- or project-centred short-term focus, while obfuscating the role of affected communities and the broader society. Therefore, apart from improving understanding of individual adaptation pathways, there is a necessity for conceptual lenses that are polycentric, dynamic and multi-scalar.

There remain major uncertainties on how climate change will affect mining regions and what specific vulnerabilities are. Additionally, despite a relatively broad geographical coverage (representing some 18 countries in the Global North and Global South), our review has revealed a clustering of studies in Canada and Australia. This is not representative of the distribution of resource extraction sites. There are many more struggles and ongoing conflicts in mining regions throughout the world (e.g., see The Environmental Justice Atlas, 2019). There is a need for more empirical data and research that address the variety of operations implicated in mining. For example, the type (surface or underground), scale (artisanal to large scale) and stage (exploration, extraction and abandoned mines) of mining need to be better integrated in order to accommodate substantial differences. There is little on deep-sea mining or offshore fossil fuel extraction in our sample of the literature.

While assessments of vulnerability to climate change and adaptive capacity in mining regions are important, studies should explore how to enable solutions that address the injustices that prevail in the sector between corporate power and those experiencing negative impacts locally and globally. There is a need in specific empirical case studies and action research to explore where new forms of engagement are developed with the enhancement of sustainability and justice as key goals. We hope that this review contributes to acknowledging multiple framings of adaptation and will contribute to the renegotiation of practices based on a reflection of how adaptation is framed.

Acknowledgements

We are grateful to Anthony Bebbington, Rauno Sairinen and reviewers for valuable comments on an earlier manuscript. Their advice helped to define more clearly the focus of the article.

Author contributions

JL and SPJB contributed equally to the design and implementation of the review and to the writing of the article.

Financial support

JL acknowledges the Australian Government Research Training Program Scholarship.

Conflict of interest

None.

Ethical standards

The manuscript is our own original work and does not duplicate any other previously published work. The manuscript has been submitted only to the journal Global Sustainability and it is not under consideration, accepted for publication or in press elsewhere. All listed authors know of and agree to the manuscript being submitted to the journal. The manuscript contains nothing that is abusive, defamatory, fraudulent, illegal, libellous or obscene.

Footnotes

1 Defined here as a broad category that includes areas spatially and socioeconomically dependent on the extraction of minerals, metals and hydrocarbons. We refer to surface mining when soil, rock, liquids and gases are removed from the deposits and to underground mining when deposits and liquids are removed through shafts and tunnels still covered by soil and rocks. This includes fracking (Bridge, Reference Bridge2016).

References

Abate, R. S. (2013). Corporate responsibility and climate justice: a proposal for a polluter-financed relocation fund for federally recognized tribes imperiled by climate change. Fordham Environmental Law Review, 25(1), 10.Google Scholar
Addison, T. (2018). Climate Change and the Extractives Sector. WIDER (Working Paper 84). United Nations University.Google Scholar
Agrawala, S., Matus Kramer, A., Prudent-Richard, G., Sainsbury, M., & Schreitter, V. (2012). Incorporating climate change impacts and adaptation in environmental impact assessments: opportunities and challenges. Climate and Development, 4(1), 2639.Google Scholar
Aleke, B. I., & Nhamo, G. (2016). Information and communication technology and climate change adaptation: Evidence from selected mining companies in South Africa. Jàmbá: Journal of Disaster Risk Studies, 8(3), 250.Google Scholar
Ali, S. H., Giurco, D., Arndt, N., Nickless, E., Brown, G., Demetriades, A., … Yakovleva, N. (2017). Mineral supply for sustainable development requires resource governance. Nature, 543(7645), 367372.Google Scholar
Auty, R. (2002). Sustaining Development in Mineral Economies: The Resource Curse Thesis. Routledge.Google Scholar
Averchenkova, A., Crick, F., Kocornik-Mina, A., Leck, H., & Surminski, S. (2016). Multinational and large national corporations and climate adaptation: are we asking the right questions? A review of current knowledge and a new research perspective. Wiley Interdisciplinary Reviews: Climate Change, 7(4), 517536.Google Scholar
Bach, M. (2019). The oil and gas sector: from climate laggard to climate leader? Environmental Politics, 28(1), 87103.Google Scholar
Bambrick, H. (2018). Resource extractivism, health and climate change in small islands. International Journal of Climate Change Strategies and Management, 10(2), 272288.Google Scholar
Bebbington, A. J., & Bury, J. (2013). Subterranean Struggles: New Dynamics of Mining, Oil, and Gas in Latin America (Vol. 8). University of Texas Press.Google Scholar
Bebbington, A. J., Bury, J., Cuba, N., & Rogan, J. (2015). Mining, risk and climate resilience in the ‘other’ Pacific: Latin American lessons for the South Pacific. Asia Pacific Viewpoint, 56(2), 189207.Google Scholar
Bendell, J. (2018). Deep Adaptation: A Map for Navigating Climate Tragedy. Retrieved from http://insight.cumbria.ac.uk/id/eprint/4166/.Google Scholar
Birch, T. (2016). Climate change, mining and traditional Indigenous knowledge in Australia. Social Inclusion, 4(1), 92101.Google Scholar
Bos, K., & Gupta, J. (2016). Inclusive development, oil extraction and climate change: a multilevel analysis of Kenya. International Journal of Sustainable Development & World Ecology, 23(6), 482492.Google Scholar
Bridge, G. (2016). Resource extraction. International Encyclopedia of Geography: People, the Earth, Environment, and Technology, 1–13. Retrieved from https://onlinelibrary.wiley.com/doi/book/10.1002/9781118786352.Google Scholar
Brock, A., & Dunlap, A. (2018). Normalising corporate counterinsurgency: engineering consent, managing resistance and greening destruction around the Hambach coal mine and beyond. Political Geography, 62, 3347.Google Scholar
BSR (2011). Adapting to Climate Change: A Guide for the Mining Industry. Retrieved from https://www.bsr.org/collaboration/groups/resilience-and-adaptation-initiative.Google Scholar
Cameron, E. S. (2012). Securing Indigenous politics: a critique of the vulnerability and adaptation approach to the human dimensions of climate change in the Canadian Arctic. Global Environmental Change, 22(1), 103114.Google Scholar
Capstick, S., Kelly, J., Barrett, A., & Penailillo, R. (2014). Incorporating climate change impacts into environmental assessments. Paper presented at the 34th Annual Conference of the International Association for Impact Assessment. Retrieved from http://conferences.iaia.org/2014/IAIA14-final-papers/Capstick,%20Sean.%20%20Incorporating%20climate%20change%20impacts%20into%20EA.pdf.Google Scholar
Carkovic, A. B., Calcagni, M. S., Vega, A. S., Coquery, M., Moya, P. M., Bonilla, C. A., & Pastén, P. A. (2016). Active and legacy mining in an arid urban environment: challenges and perspectives for Copiapó, Northern Chile. Environmental Geochemistry and Health, 38(4), 10011014.Google Scholar
Carlson, C., Goldman, G., & Dahl, K. (2016). Stormy seas, rising risks: assessing undisclosed risk from sea level rise and storm surge at coastal US oil refineries. In Drake, L. J., Kontar, Y. Y., Eichelberger, C. J., Rupp, S. T., & Taylor, M. K. (eds), Communicating Climate-Change and Natural Hazard Risk and Cultivating Resilience: Case Studies for a Multi-disciplinary Approach (pp. 295308). Springer International Publishing.Google Scholar
Curley, A. (2018). A failed green future: Navajo Green Jobs and energy ‘transition’ in the Navajo Nation. Geoforum, 88, 5765.Google Scholar
Damian, M. (2014). Mauvaise nouvelle pour le climat et les peuples de l'Amazonie équatorienne: l'abandon du projet Yasuni-ITT de gel du pétrole en terre. Natures Sciences Sociétés, 21(4), 428435.Google Scholar
Damigos, D. (2012). Monetizing the impacts of climate change on the Greek mining sector. Mitigation and Adaptation Strategies for Global Change, 17(8), 865878.Google Scholar
Duerden, F., Pearce, T., Ford, J., & Pittman, J. (2014). Case Studies of Climate Change in the Yukon Mining Sector: From Planning and Operation to Remediation and Restoration. Climate Change Impacts and Adaptation Division.Google Scholar
Dyer, J., Leventon, J., Stringer, L., Dougill, A., Syampungani, S., Nshimbi, M., … Kafwifwi, A. (2013). Partnership models for climate compatible development: experiences from Zambia. Resources, 2(1), 125.Google Scholar
Eisenstadt, T. A., & West, K. J. (2016). Indigenous belief systems, science, and resource extraction: climate change attitudes in Ecuador. Global Environmental Politics, 17(1), 4058.Google Scholar
The Environmental Justice Atlas (2019). World map. Retrieved from https://ejatlas.org.Google Scholar
Evans, G. (2007). A just transition from coal to renewable energy in the Hunter Valley of New South Wales, Australia. International Journal of Environment, Workplace and Employment, 3(3–4), 175194.Google Scholar
Evans, G. (2008). Transformation from ‘carbon valley’ to a ‘post-carbon society’ in a climate change hot spot: the coalfields of the Hunter Valley, New South Wales, Australia. Ecology and Society, 13(1). Retrieved from http://www.ecologyandsociety.org/vol13/iss1/art39/.Google Scholar
Evans, G., & Phelan, L. (2016). Transition to a post-carbon society: linking environmental justice and just transition discourses. Energy Policy, 99, 329339.Google Scholar
Ford, J. D., Pearce, T., Prno, J., Duerden, F., Berrang Ford, L., Beaumier, M., & Smith, T. (2010). Perceptions of climate change risks in primary resource use industries: a survey of the Canadian mining sector. Regional Environmental Change, 10(1), 6581.Google Scholar
Ford, J. D., Pearce, T., Prno, J., Duerden, F., Ford, L. B., Smith, T. R., & Beaumier, M. (2011). Canary in a coal mine: perceptions of climate change risks and response options among Canadian mine operations. Climatic Change, 109(3–4), 399415.Google Scholar
Füssel, H. M. (2007). Adaptation planning for climate change: concepts, assessment approaches, and key lessons. Sustainability Science, 2(2), 265275.Google Scholar
Geels, F. W. (2005). Technological Transitions and System Innovations: A Co-evolutionary and Socio-technical Analysis. Edward Elgar.Google Scholar
Gera, W. (2016). Examining the resilience of public participation structures for sustainable mining in the Philippines. In Mauerhofer, V. (ed.), Legal Aspects of Sustainable Development: Horizontal and Sectoral Policy Issues (pp. 203231). Springer International Publishing.Google Scholar
Gillard, R., Gouldson, A., Paavola, J., & Van Alstine, J. (2016). Transformational responses to climate change: beyond a systems perspective of social change in mitigation and adaptation. Wiley Interdisciplinary Reviews: Climate Change, 7(2), 251265.Google Scholar
Giurco, D., & Cooper, C. (2012). Mining and sustainability: asking the right questions. Minerals Engineering, 29, 312.Google Scholar
Hadarits, M., Pittman, J., Corkal, D., Hill, H., Bruce, K., & Howard, A. (2017). The interplay between incremental, transitional, and transformational adaptation: a case study of Canadian agriculture. Regional Environmental Change, 17(5), 15151525.Google Scholar
Hilson, G. (2002). An overview of land use conflicts in mining communities. Land Use Policy, 19(1), 6573.Google Scholar
Hirons, M., Hilson, G., Asase, A., & Hodson, M. E. (2014). Mining in a changing climate: what scope for forestry-based legacies? Journal of Cleaner Production, 84, 430438.Google Scholar
Hodgkinson, J., Hobday, A. J., & Pinkard, E. A. (2014). Climate adaptation in Australia's resource-extraction industries: ready or not? Regional Environmental Change, 14(4), 16631678.Google Scholar
Hodgkinson, J., Littleboy, A., Howden, M., Moffat, K., & Loechel, B. (2010). Climate Adaptation in the Australian Mining and Exploration Industries. Climate Adaptation Flagship Working Paper.Google Scholar
Hodgkinson, J. H., & Smith, M. H. (2018). Climate change and sustainability as drivers for the next mining and metals boom: the need for climate-smart mining and recycling. Resources Policy. doi:10.1016/j.resourpol.2018.05.016.Google Scholar
Hoffmann, A. A., & Sgro, C. M. (2011). Climate change and evolutionary adaptation. Nature, 470(7335), 479485.Google Scholar
ICC (2011). A Circumpolar Inuit Declaration on Resource Development Principles in Inuit Nunaat. Retrieved from http://inuit.org/about-icc/icc-declarations/declaration-on-resource-development-principles-2011.Google Scholar
ICMM (2013). Adapting to a Changing Climate: Implications for the Mining and Metals Industry. Retrieved from https://www.icmm.com/en-gb/publications/climate-change/adapting-to-a-changing-climate-implications-for-the-mining-and-metals-industry.Google Scholar
IPCC (2014). Climate change 2014: impacts, adaptation, and vulnerability. Part A: global and sectoral aspects. In Field, C. B., Barros, V. R., Dokken, D. J., Mach, K. J., Mastrandrea, M. D., Bilir, T. E., … White, L. L. (eds), Contribution of Working Group II to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change (p. 1132). Cambridge University Press.Google Scholar
IPIECA (2013). Addressing Adaptation in the Oil and Gas Industry. Retrieved from http://www.ipieca.org/news/addressing-adaptation-in-the-oil-and-gas-industry/.Google Scholar
IPIECA (2016). IPIECA Climate Change Reporting Framework: A Pilot Guidance Document for the Oil and Gas Industry. Retrieved from http://www.ipieca.org/resources/good-practice/ipieca-climate-change-reporting-framework.Google Scholar
Irarrázabal, R. (2006). Mining and climate change: towards a strategy for the industry. Journal of Energy & Natural Resources Law, 24(3), 403422.Google Scholar
Jegede, A. O. (2016). The environmental and economic implications of the climate change and extractive industry nexus in Africa. Environmental Economics, 7(4), 95103.Google Scholar
Kemp, D., Owen, J. R., Gotzmann, N., & Bond, C. J. (2011). Just relations and company–community conflict in mining. Journal of Business Ethics, 101(1), 93109.Google Scholar
Kolk, A., & Levy, D. (2001). Winds of change: corporate strategy, climate change and oil multinationals. European Management Journal, 19(5), 501509.Google Scholar
Kronenberg, J. (2013). Linking ecological economics and political ecology to study mining, glaciers and global warming. Environmental Policy & Governance, 23(2), 7590.Google Scholar
Kuemmerle, T., Baskin, L., Leitão, P., Prishchepov, A., Thonicke, K., & Radeloff, V. (2014). Potential impacts of oil and gas development and climate change on migratory reindeer calving grounds across the Russian Arctic. Diversity and Distributions, 20(4), 416429.Google Scholar
Leach, M., Reyers, B., Bai, X., Brondizio, E. S., Cook, C., Díaz, S., … Subramanian, S. M. (2018). Equity and sustainability in the Anthropocene: a social–ecological systems perspective on their intertwined futures. Global Sustainability, 1, e13.Google Scholar
Leventon, J., Dyer, J. C., & Van Alstine, J. D. (2015). The private sector in climate governance: opportunities for climate compatible development through multilevel industry–government engagement. Journal of Cleaner Production, 102, 316323.Google Scholar
Loechel, B., Hodgkinson, J., & Moffat, K. (2013). Climate change adaptation in Australian mining communities: comparing mining company and local government views and activities. Climatic Change, 119(2), 465477.Google Scholar
Magnan, A. K., Schipper, E. L. F., Burkett, M., Bharwani, S., Burton, I., Eriksen, S., … Ziervogel, G. (2016). Addressing the risk of maladaptation to climate change. Wiley Interdisciplinary Reviews: Climate Change, 7(5), 646665.Google Scholar
Manley, D., Cust, J., & Cecchinato, G. (2016). Stranded Nations? The Climate Policy Implications for Fuel-Rich Developing Countries. Policy Paper 34. OxCarre.Google Scholar
Martinez-Alier, J., & Temper, L. (2007). Oil and climate change: voices from the south. Economic and Political Weekly, 42(50), 1619.Google Scholar
Martus, E. (2019). Russian industry responses to climate change: the case of the metals and mining sector. Climate Policy, 19, 1729.Google Scholar
Maru, Y. T., Chewings, V., & Sparrow, A. (2012). Climate Change Adaptation, Energy Futures and Carbon Economies in Remote Australia: A Review of the Current Literature, Research and Policy. Working Paper CW005. Ninti One Ltd.Google Scholar
Mason, L., & Giurco, D. (2013). Climate Change Adaptation for Australian Minerals Industry Professionals. National Climate Change Adaptation Research Facility.Google Scholar
McGlade, C., & Ekins, P. (2015). The geographical distribution of fossil fuels unused when limiting global warming to 2°C. Nature, 517(7533), 187190.Google Scholar
Naess, L. O., Newell, P., Newsham, A., Phillips, J., Quan, J., & Tanner, T. (2015). Climate policy meets national development contexts: insights from Kenya and Mozambique. Global Environmental Change, 35, 534544.Google Scholar
Navarro, H. F. (2017). Glaciares del semiárido chileno en el contexto de cambio climático y explotación minera. Espacios, 7(13), 1726.Google Scholar
Newman, M. E., & Park, J. (2003). Why social networks are different from other types of networks. Physical Review E, 68(3), 036122.Google Scholar
Newton, J., Paci, C. J., & Ogden, A. (2005). Climate change and natural hazards in northern Canada: integrating indigenous perspectives with government policy. In Haque, C. E. (ed.), Mitigation of Natural Hazards and Disasters: International Perspectives (pp. 209239): Springer.Google Scholar
Northey, S. A., Mudd, G. M., Werner, T. T., Jowitt, S. M., Haque, N., Yellishetty, M., & Weng, Z. (2017). The exposure of global base metal resources to water criticality, scarcity and climate change. Global Environmental Change, 44, 109124.Google Scholar
Nunfam, V. F., Oosthuizen, J., Adusei-Asante, K., Van Etten, E. J., & Frimpong, K. (2019). Perceptions of climate change and occupational heat stress risks and adaptation strategies of mining workers in Ghana. Science of the Total Environment, 657, 365378.Google Scholar
Nunfam, V. F., Van Etten, E. J., Oosthuizen, J., Adusei-Asante, K., & Frimpong, K. (2019). Climate change and occupational heat stress risks and adaptation strategies of mining workers: perspectives of supervisors and other stakeholders in Ghana. Environmental Research, 169, 147155.Google Scholar
Nuttall, M. (2012). Imagining and governing the Greenlandic resource frontier. The Polar Journal, 2(1), 113124.Google Scholar
O'Brien, K. (2012). Global environmental change II: from adaptation to deliberate transformation. Progress in Human Geography, 36(5), 667676.Google Scholar
O'Rourke, D., & Connolly, S. (2003). Just oil? The distribution of environmental and social impacts of oil production and consumption. Annual Review of Environment and Resources, 28(1), 587617.Google Scholar
Odell, S. D., Bebbington, A., & Frey, K. E. (2018). Mining and climate change: a review and framework for analysis. The Extractive Industries and Society, 5(1), 201214.Google Scholar
Orta-Martínez, M., & Finer, M. (2010). Oil frontiers and Indigenous resistance in the Peruvian Amazon. Ecological Economics, 70(2), 207218.Google Scholar
Park, S., Marshall, N. A., Jakku, E., Dowd, A.-M., Howden, S. M., Mendham, E., & Fleming, A. (2012). Informing adaptation responses to climate change through theories of transformation. Global Environmental Change, 22(1), 115126.Google Scholar
Patterson, J. J., Thaler, T., Hoffmann, M., Hughes, S., Oels, A., Chu, E., … Jordan, A. (2018). Political feasibility of 1.5°C societal transformations: the role of social justice. Current Opinion in Environmental Sustainability, 31, 19.Google Scholar
Pearce, T., Ford, J. D., Prno, J., & Duerden, F. (2009). Climate Change and Canadian Mining: Opportunities for Adaptation. David Suzuki Foundation.Google Scholar
Pearce, T., Ford, J. D., Prno, J., Duerden, F., Pittman, J., Beaumier, M., … Smit, B. (2011). Climate change and mining in Canada. Mitigation and Adaptation Strategies for Global Change, 16(3), 347368.Google Scholar
Pellegrini, L., Arsel, M., Falconí, F., & Muradian, R. (2014). The demise of a new conservation and development policy? Exploring the tensions of the Yasuní ITT initiative. The Extractive Industries and Society, 1(2), 284291.Google Scholar
Pellegrino, C., & Lodhia, S. (2012). Climate change accounting and the Australian mining industry: exploring the links between corporate disclosure and the generation of legitimacy. Journal of Cleaner Production, 36, 6882.Google Scholar
Pelling, M. (2011). Adaptation to Climate Change: From Resilience to Transformation. Routledge.Google Scholar
Petheram, L., Zander, K., Campbell, B., High, C., & Stacey, N. (2010). ‘Strange changes’: Indigenous perspectives of climate change and adaptation in NE Arnhem Land (Australia). Global Environmental Change, 20(4), 681692.Google Scholar
Petticrew, M., & Roberts, H. (2008). Systematic Reviews in the Social Sciences: A Practical Guide: John Wiley & Sons.Google Scholar
Phillips, J. (2016). Climate change and surface mining: a review of environment–human interactions and their spatial dynamics. Applied Geography, 74, 95108.Google Scholar
PIDF (2015). SUVA Declaration on Climate Change. Retrieved from http://pacificidf.org/suva-declaration-on-climate-change/.Google Scholar
Piggot, G. (2018). The influence of social movements on policies that constrain fossil fuel supply. Climate Policy, 18(7), 942954.Google Scholar
Pizarro, J., Sainsbury, B., Hodgkinson, J., & Loechel, B. (2017). Australian uranium industry climate change vulnerability assessment. Environmental Development, 24, 109123.Google Scholar
Prowse, T. D., Furgal, C., Chouinard, R., Melling, H., Milburn, D., & Smith, S. L. (2009). Implications of climate change for economic development in northern Canada: energy, resource, and transportation sectors. AMBIO: A Journal of the Human Environment, 38(5), 272281.Google Scholar
Raskin, P., Banuri, T., Gallopin, G., Gutman, P., Hammond, A., Kates, R., & Swart, R. (2002). Great Transition: The Promise and Lure of the Times Ahead. Stockholm Environment Institute.Google Scholar
SaveTheArctic (2017). The Climate Lawsuit against the Norwegian Government. Retrieved from https://www.savethearctic.org/en/peoplevsarcticoil/background-documents/.Google Scholar
Segura-Salazar, J., & Tavares, L. (2018). Sustainability in the minerals industry: seeking a consensus on its meaning. Sustainability, 10(5), 1429.Google Scholar
Seoane, J., Taddei, E., Algranati, C., & Borón, A. (2013). Extractivismo, despojo y crisis climática: Desafíos para los movimientos sociales y los proyectos emancipatorios de nuestra América. Ediciones Herramienta.Google Scholar
Sharma, V. (2017). Mining and climate change. In O'Callaghan, T. & Graetz, G. (eds), Mining in the Asia-Pacific (pp. 301320). Springer.Google Scholar
Sharma, V., & Franks, D. M. (2013). In situ adaptation to climatic change: mineral industry responses to extreme flooding events in Queensland, Australia. Society & Natural Resources, 26(11), 12521267.Google Scholar
Slezak, M. (2016). Marrakech climate talks: giving the fossil fuel lobby a seat at the table. The Guardian. Retrieved from https://www.theguardian.com/environment/2016/nov/07/marrakech-climate-talks-giving-the-fossil-fuel-lobby-a-seat-at-the-table.Google Scholar
Smit, B., & Wandel, J. (2006). Adaptation, adaptive capacity and vulnerability. Global Environmental Change, 16(3), 282292.Google Scholar
Stensrud, A. B. (2016). Harvesting water for the future: reciprocity and environmental justice in the politics of climate change in Peru. Latin American Perspectives, 43(4), 5672.Google Scholar
Sternberg, T., & Chatty, D. (2016). Marginality, climate and resources in pastoral rangelands: Oman and Mongolia. Rangelands, 38(3), 145151.Google Scholar
Taylor, M. (2015). The Political Ecology of Climate Change Adaptation: Livelihoods, Agrarian Change and the Conflicts of Development. Routledge.Google Scholar
Thornton, T. F., & Comberti, C. (2017). Synergies and trade-offs between adaptation, mitigation and development. Climatic Change, 140(1), 518.Google Scholar
Tost, M., Hitch, M., Chandurkar, V., Moser, P., & Feiel, S. (2018). The state of environmental sustainability considerations in mining. Journal of Cleaner Production, 182, 969977.Google Scholar
UNFCCC (1992). United Nations Framework Convention on Climate Change. Retrieved from https://unfccc.int/files/essential_background/background_publications_htmlpdf/application/pdf/conveng.pdf.Google Scholar
UNFCCC (2015). The Paris Agreement. Retrieved from http://unfccc.int/resource/docs/2015/cop21/eng/l09r01.pdf.Google Scholar
UNSDSN (2015). Transforming Our World: The 2030 Agenda for Sustainable Development. Retrieved from http://unsdsn.org/resources/publications/an-action-agenda-for-sustainable-development/.Google Scholar
Verweij, M., Douglas, M., Ellis, R., Engel, C., Hendriks, F., Lohmann, S., … Thompson, M. (2006). Clumsy solutions for a complex world: the case of climate change. Public Administration, 84(4), 817843.Google Scholar
Vidal, J. (2016). World's largest carbon producers face landmark human rights case. The Guardian. Retrieved from https://www.theguardian.com/environment/2016/jul/27/worlds-largest-carbon-producers-face-landmark-human-rights-case.Google Scholar
Waddell, S., Waddock, S., Cornell, S., Dentoni, D., McLachlan, M., & Meszoely, G. (2015). Large systems change: an emerging field of transformation and transitions. Journal of Corporate Citizenship, 58, 530.Google Scholar
WEF (2016). Mapping Mining to the Sustainable Development Goals: An Atlas. Retrieved from http://unsdsn.org/resources/publications/mapping-mining-to-the-sustainable-development-goals-an-atlas/.Google Scholar
Figure 0

Table 1. Adaptation pathways (adapted from Pelling, 2011).

Figure 1

Fig. 1. Selected articles representative of Pelling's typology of adaptation pathways, year of publication and geographical coverage. Each line represents an individual article colour-coded depending on the classification into one of the three adaptation pathways. N/S = non-specified.

Figure 2

Table 2. Adaptation pathways in mining regions.