Fossil fuel supply, green growth, and unburnable carbon
Transcription
Fossil fuel supply, green growth, and unburnable carbon
DISCUSSION BRIEF Fossil fuel supply, green growth, and unburnable carbon Findings such as these raise questions about the implications and wisdom of further investments in fossil fuel supply infrastructure. What are the long-term emissions consequences of major new investments in unconventional oil and gas development, or in new coal mines A semi-submersible oil drilling rig in the Arctic. and ports? Who is accounting for these consequences in financial markets or in long-term planning, especially in countries that are increasUnburnable carbon and lock-in: two key concepts ingly focused on green growth and Low Emissions DevelopAbsent remarkably rapid advances in CCS, any serious efment Strategies (LEDS)? And if countries move decisively to fort to mitigate climate change will require leaving the large reduce global emissions, who gets to benefit from exploiting majority of fossil fuel assets in the ground. This notion of the remaining fossil fuel budget? “unburnable carbon” – that proven fossil fuel reserves may not be useable – has gained increasing currency, visible in reSEI is exploring these and other questions through case cent publications and speeches by leaders of the IEA and the studies and by developing new analytical and accounting Organisation for Economic Co-operation and Development frameworks. The work is based on three premises. The first (Gurría 2013). Spurred by the work of the Carbon Tracker is that world leaders need to enact policies and measures Initiative, financial institutions and advisors have also begun that substantially curtail global CO2 emissions – and they examining the implications of carbon constraints on capital will ultimately succeed in doing so. As daunting and wishmarkets, and the financial risks posed by potentially signififul as that premise may seem, it is useful to note that many major energy companies already assume a significant price Risks of and responses to the on carbon in their future business planning (CDP 2013). The new fossil fuel economy second premise is that despite its promise to turn high-carbon fossil fuels, especially coal, into low-carbon resources, carbon capture and storage (CCS) will not be widely deThis discussion brief is part of a two-year SEI project that aims to deepen understanding of the risks ployed in the coming decades. Progress on CCS has been posed by new investments in fossil fuel infrastrucmuch slower than hoped, and many barriers and uncertainture, and of the possible responses by policy-makers ties remain. Without widespread CCS, a low-carbon future and civil society to mitigate or avoid these risks. In will severely constrain fossil fuel exploitation. The third particular, this initiative examines major decisions premise is that policies to slow or limit fossil fuel extracregarding new investments in fossil fuel extraction tion, not just fossil fuel use, will be needed. This is an area and trade infrastructure, especially in venues where that has so far been largely overlooked in efforts to mitigreen growth or low-emission development strategate climate change. New analytical tools and approach are gies (LEDS) are under development or consideraneeded to help policy-makers understand the implications of tion. Our aim is to provide resources and tools to new fossil fuel supply infrastructure. 1 See, for example, McDonald, F. (2013). Two-thirds of energy sector will have to be left undeveloped, Bonn conference told. The Irish Times, 12 June. http://www.irishtimes.com/news/world/europe/two-thirds-of-energy-sectorwill-have-to-be-left-undeveloped-bonn-conference-told-1.1425009. help planners and policy-makers assess the risks of, and responses to, fossil development, as part of low-carbon and green growth planning. © Olav Gjerstad / Flickr Introduction In mid-2013, International Energy Agency Chief Economist Fatih Birol made headlines by warning energy executives, investors, and national climate change negotiators that “about two-thirds of all proven reserves of oil, gas and coal will have to be left undeveloped if the world is to achieve the goal of limiting global warming at two degrees Celsius.”1 Furthermore, the IEA has found that enough new infrastructure is slated to come online by 2017 to lock in the remainder of CO2 emissions allowable under a 2°C limit (IEA 2012c). 2035 Global Enregy Production (EJ) 800 vs. 2050 in WEO) and richer regional detail. As shown in Figure 1, in both the WEO 2012 (450) and GEA (Mix) lowcarbon scenarios, total energy use declines to nearly half of business-as-usual levels by 2035. These declines are most pronounced for coal and unconventional oil resources. 600 400 200 0 WEO 2012 WEO 2012 (Current Policies) (450) WEO 2012 (Baseline) WEO 2012 (Mix) Coal, All Gas, Unconventional Gas, Conventional Oil, Unconventional Oil, Conventional Figure 1: Comparison of fossil fuel production by resource type and scenario for 2035 WEO 2012 and GEA. The GEA Mix scenario represents a balance between the GEA’s more purely efficiency-driven and more “clean supply” driven scenarios. cant overvaluation of fossil fuel assets (HSBC 2012; HSBC 2013; Goldman Sachs 2013; Rystad Energy 2013). Another key concept is that of “lock-in”: that once fossil fuel infrastructure is built, it becomes difficult to avoid fully using it throughout its full economic lifetime. Lock-in is both a financial and a political economy phenomenon: as new infrastructure is built, and capital investments are financed, marginal costs of production drop, and incumbent interests will act to ensure its continued operation. Supplyside investments in expanding fossil fuel extraction (e.g. coal mines, gas and oil deposits) render economies and societies reliant upon and thus supportive of fossil fuels, creating the economic and political constituencies that perpetuate global high-emission pathways. A prime example is Canada’s oil sands development, which has transformed the country’s domestic politics and helped precipitate an end to its international climate leadership. IEA analysis suggests the scale of lock-in already in place: the continued operation of existing energy infrastructure – from power plants to oil wells – alone would emit 80% of the CO2 emissions allowable through the year 2035 under a 2°C goal (IEA 2012c). This finding suggests limited “room” for new fossil fuel infrastructure. Such “room” could be expanded if existing infrastructure were abandoned before the end of its useful life. However, this seems unlikely given the generally lower cost of continuing production at existing facilities relative to building new ones. Indeed, the IEA’s scenario for a 2°C emissions pathway does not envision the stranding of any oil or gas reserves that already undergone development (IEA 2013b); most of the fossil fuels that would need to be left in the ground are new – unconventional oil and gas as well as yet-to-be-exploited coal. To get a more detailed picture of what a global carbon budget might mean for fossil fuel production and reserves, we look to the work of the Global Energy Assessment (GEA 2012). While similar in many respects to IEA’s World Energy Outlook – both develop low-carbon scenarios that adhere roughly to a 2°C limit – the GEA has a longer time-horizon (to 2100 As we look out to the year 2100, the potential longer-term implications of a 2°C constraint become clearer: coal and unconventional oil – the most carbon-intensive of five resource categories shown – are the predominant resources that would be stranded in a low-carbon world, as illustrated in Figure 2.2 These are also the classes of fossil fuel resources that, collectively, provide less net social benefit as compared with conventional oil and gas resources. The economic rents (i.e. profits) per unit energy and per unit of greenhouse gases (GHGs) tend to be lower, as their production costs are closer, on average, to market prices, and the external costs per unit energy and GHG are also far higher (Collier and Venables 2013). These conclusions are unlikely to differ dramatically under a less ambitious emission reduction target, such as a 3°C or 4°C limit. Thus, barring a surge in CCS deployment, the vast majority of coal reserves and most unconventional oil resources (proven or otherwise) would need to be left in the ground at least through 2100. Consequently, these resources (coal, unconventional oil) are a principal focus of our project. We will use case studies to examine the implications of tapping oil shale, the most significant of all unconventional oil resources, in Utah (U.S.), Estonia and Jordan, as well as to examine the expansion of coal mine and export infrastructure in the Pacific coal market, and oil sands and heavy deposits in the Orinoco Basin of Colombia. The fossil fuel industry continues to expand In the face of the constraints that eventual climate action would impose, and the risk of a carbon asset “bubble”, new fossil fuel extraction and infrastructure investment continue to grow rapidly. Upstream oil and gas sector investment increased 20% between 2008 and 2012, and is projected to remain at high levels – nearly $700 billion per year – for the next two decades (IEA 2013c). Despite a major shift from coal to gas in the U.S., coal remains the fastest-growing fossil fuel globally. The expected growth in coal use from 2012 to 2017 (1.2 billion tonnes per year) is equal to the current coal consumption in Russia and the United States combined (IEA 2012b). The IEA also projects that 40% of growth in coal production over the current decade will be destined for interregional exports, largely to meet demands in India and China (IEA 2012c). Major new investments in coal mines and ports are under way or being considered in Australia, Indonesia, Russia, South Africa, Colombia, and the U.S. (IEA 2012a). Just as forces of technological innovation have led to remarkable advances in renewable energy and energy efficiency, they have also enabled continued growth in fossil fuel supply, particularly for oil and gas, and have made fossil fuels ever harder to displace. These innovations include 3-D seismic 2 Note that recent analysis by SEI and partners (Baer et al. 2013) suggests that pathways commonly described as 2°C-compatible actually correspond to less than a 50% chance of staying below 2°C per the latest Intergovernmental Panel on Climate Change estimates (IPCC 2013). “The 2oC budget” Produced within the 2oC budget Produced under BAU scenario Produced beyond the 2oC budget Coal 8,700 Oil, Unconventional 7,300 Remaining resources Gas, Unconventional Additional production 2010-2100, GEA Baseline scenario Oil, Conventional Production 2010-2100, GEA Mix scenario Historical production (through 2010) Gas, Conventional 1,000 500 0 500 1,000 1,500 2,000 2,500 3,000 3,500 4,000 Carbon content (Gt CO2) of fossil fuel resources Figure 2: Fossil fuels exploited vs. left in the ground, through 2100, relative to a 2°C emissions budget, in terms of CO2 emissions resulting from fuel use. Drawing from data on historical fossil fuel use (IEA 2013a), fossil fuel reserves and resources (GEA 2012), and projected fossil fuel use under GEA’s Mix and Baseline scenarios, this figure shows the amounts of five categories of fossil fuel – conventional natural gas, conventional oil, unconventional gas, unconventional oil, and coal – that have been burned (pale pink bars) and could still be exploited and combusted through 2100 (pale purple bars) under a scenario (GEA Mix) that represents at least a 50% chance of staying within 2°C. The dark pink bars illustrate the additional amounts of fossil fuels exploited and combusted through 2100 under a business-as-usual scenario (GEA Baseline). The dark purple bars represent the amount of additional recoverable resources. As shown, the vast majority of the resources left in the ground as the result of achieving a 2°C target would be coal and unconventional oil. imaging, horizontal drilling, multi-stage hydraulic fracturing, and process controls for deep-water projects, which, together with higher oil prices, have made production in previously inaccessible regions such as Brazil’s pre-salt fields and Venezuela’s extra-heavy oil deposits not only feasible but profitable (U.S. EIA 2013). In part because of such advances, Venezuela recently overtook Saudi Arabia in terms of proven oil reserves. © Travis S. / Flickr Major fossil fuel infrastructure development or expansion projects are also under way or being considered in many countries. According to a recent Ecofys report for Greenpeace International, 14 upstream projects could supply “29,400 billion cubic meters of natural gas, 260,000 million barrels of oil and 49,600 million tonnes of coal”, which might lead to 300 gigatonnes of CO2-equivalent emissions between 2012 and 2050, or 20 to 33% of the remaining carbon budget under a 2°C target (Meindertsma and Blok 2012). These projects range from deep-water oil drilling in Mexico and Brazil and oil sands extraction in Canada and Venezuela, to coal mining and export in the U.S. and Australia. The Trans-Alaska Pipeline System, built in the 1970s, conveys oil from the Prudhoe Bay oil field. A major gap in in low-emissions development and green growth planning If global climate objectives such as a 2°C limit are seriously pursued, many new and existing fossil fuel supply investments could be stranded, with potentially significant negative consequences for global financial markets. Indeed, some economists have argued that if countries hold to agreements to meet such a target, financial markets will have seriously overvalued coal, oil, and gas assets, leading to a “carbon bubble” (Carbon Tracker Initiative 2011; Carbon Tracker Initiative 2011; Leaton et al. 2013; HSBC 2013; Hsueh and Lewis 2013; Gurría 2013). Detailed analyses of these issues have so far focused only on publicly traded companies, but many governments appear to face similar risks: about three quarters of proven reserves, as measured by carbon content, are held by governmentowned companies (IEA 2012c). At the same time, proposals for new fossil fuel infrastructure are increasingly controversial in many coun- © Jon Fischer / Flickr Coal mining along a river in East Kalimantan, Indonesia. tries. Concern over the emissions consequences of U.S. West Coast coal export terminals and the Keystone XL pipeline has galvanized climate change activism in North America. Resource competition, and concerns over local social and environmental impacts have motivated communities in India, Indonesia, China, and elsewhere to slow the building of coal mines and coal-fired power plants (Sierra Club 2011; 2012). The sizable water requirements of many unconventional oil and gas extraction and processing technologies have also created resource concerns and conflicts in the development of oil sands in Western North America and oil shale deposits in Estonia, Jordan, and Utah (Water in the West 2013). Green growth planning efforts and LEDS studies have been remarkably silent on the question of new fossil fuel supply infrastructure, despite its growing importance and relevance to sustainability and climate change. Under way in over 40 developing countries, these efforts tend to focus instead on promoting cleaner energy production and more efficient energy use. Many similar analyses and processes, from sustainable development scenarios to low-carbon plans, have been conducted in developed countries as well. We have reviewed nearly two dozen green growth and LEDS guidance documents, as well as 40 countryspecific studies, and have found almost no consideration of the emissions implications of continued fossil fuel infrastructure development (beyond the direct emissions of production facilities) or of scenarios that consider reorienting economic growth away from fossil fuel extraction and supply infrastructure expansion. A notable exception is Norway, a major fossil fuel exporter, where an active debate is emerging on future reliance on fossil fuel development and revenues. The Norwegian Ministry of the Environment recently commissioned a study to examine the potential consequences for petroleum exploration and development of a 2°C scenario (Rystad Energy 2013). The limited consideration given to the emissions consequences of fossil fuel supply is hardly surprising. Fossil fuel development is often viewed as a way to enhance energy security and promote economic development – even though in many countries it has come with a “resource curse”, or more recently the “carbon curse”, whereby benefits are unevenly distributed, other industries become uncompetitive, and broader development objectives are undermined (Sachs and Warner 2001; Frankel 2010; van der Ploeg 2011; Barma et al. 2011; Bjorvatn et al. 2012; Friedrichs and Inderwildi 2013). Furthermore, the predominant GHG emissions accounting frameworks count only the emissions that occur within the boundaries of a given jurisdiction. As a result, the consequences of expanding fossil fuel supply may be quite limited, especially where these supplies are exported or substitute for imports. Given that fossil fuel supply investments are often major elements of countries’ expected economic growth, their emissions implications tend to be left unquestioned, except to explore energy efficiency improvements and (potentially profitable) methane gas capture. In addition, the impacts of new fossil fuel supply on global GHG emissions are comparatively less well understood, and accounting frameworks and climate policies have yet to come fully to grips with how to address these emissions. New tools to address the supply side New and alternative frameworks for GHG emissions accounting and analysis can help to bring supply side considerations, and potential policy approaches, into the focus of analysts, planners, and decision-makers. Our hypothesis is that this can then lead to more effective and comprehensive strategies to reducing global GHG emissions. One such framework is extraction-based emissions accounting, which we explored in another discussion brief from this project (Erickson and Lazarus 2013a). In another brief, we looked at multiple perspectives for assessing the emissions implications of new fossil fuel infrastructure – assessments that are now only rarely undertaken (Erickson and Lazarus 2013b). By developing and testing these and other tools more fully, we seek to understand whether they can help to bring new insights and, on a practical level, identify and advance policy options to address gaps and weakness in current emission reduction efforts. To date, climate change policies and actions have focused largely on the demand side of the fossil fuel equation – tax- ing or regulating carbon where fossil fuels are consumed, promoting alternatives such as renewable energy, or encouraging more efficient fossil fuel use. While such policies and actions can be highly successful in some cases (particularly in spurring more efficient vehicles and appliances, and wind and solar technologies), they also face systemic challenges. The prospect of stringent demand-side climate policies in the future – as reflected in steeply rising carbon prices – could accelerate the extraction and use of fossil fuels in the near term, undermining the benefits of these policies. This potential outcome has been termed the “green paradox” (Sinn 2009; 2012) or “inter-temporal leakage” (Collier and Venables 2013). Some have questioned the conditions under which it might occur (Edenhofer and Kalkuhl 2011; Grafton et al. 2012; van der Ploeg and Withagen 2013). Supplyside policies and actions could reduce the risks of a green paradox, as well as of international leakage (due to nonuniform adoption of climate policies and carbon prices), while providing new options for policy-makers to consider (Collier and Venables 2013). References Some supply-side policies have been under consideration for some time, most notably the reduction of existing subsidies for fossil fuel production; estimates of the scale of global fossil fuel production subsidies vary from $80 to $285 billion per year, for developing and emerging countries alone (Bast et al. 2012). Restrictions on lending for fossil fuel supply projects by domestic and international finance institutions have also been proposed, and in some cases, adopted. Like recent initiatives to promote divestment from fossil fuel companies and to address potential overvaluation of fossil fuel assets, these efforts aim to dissuade investment by increasing the cost of capital and stigmatizing fossil fuel assets and asset holders (Ansar et al. 2013). Carbon Tracker Initiative (2011). Unburnable Carbon – Are the World’s Financial Markets Carrying a Carbon Bubble? London. http://www. carbontracker.org/carbonbubble. Other approaches aim more directly to keep fossil fuel assets in the ground. The Yasuni-ITT initiative is the most prominent example; the government of Ecuador promised to keep nearly a billion barrels of heavy crude oil buried in perpetuity under Yasuni National Park if it could raise $3.6 billion in international contributions – about half of the projected earnings (Finer et al. 2010; Davidsen and Kiff 2013). In August 2013, President Rafael Correa announced he was abandoning the initiative, after having raised only about $13 million.3 Economists have recently proposed policy approaches to close down coal mining operations, using oil rents to compensate affected parties (Harstad 2012; Collier and Venables 2013). Others have suggested strategies to avoid a green paradox, such as using internationally harmonized source taxes on capital income to dissuade near-term extraction (Sinn 2012). Supply-side policies and actions to address climate change are, for the most part, still in their infancy. Like supplyside analytical frameworks, however, they could prove to be valuable tools in helping to create effective lowcarbon pathways. Through upcoming work, we intend to investigate the potential strengths and limitations of these supply-side approaches. 3 See, e.g., BBC News (2013). Ecuador approves Yasuni park oil drilling in Amazon rainforest. 16 August. http://www.bbc.co.uk/news/world-latin-america-23722204. Ansar, A., Caldecott, B. and Tilbury, J. (2013). Stranded Assets and the Fossil Fuel Divestment Campaign: What Does Divestment Mean for the Valuation of Fossil Fuel Assets? Stranded Assets Programme. Smith School of Enterprise and the Environment, University of Oxford, Oxford, UK. http://www.smithschool.ox.ac.uk/research/stranded-assets/SAPdivestment-report-final.pdf. Baer, P., Athanasiou, T. and Kartha, S. (2013). The Three Salient Global Mitigation Pathways Assessed in Light of the IPCC Carbon Budgets. SEI discussion brief. Stockholm Environment Institute, Somerville, MA, US. http://www.sei-international.org/publications?pid=2424. Barma, N., Kaiser, K., Le, T. M. and Viñuela, L. (2011). Rents to Riches? The Political Economy of Natural Resource-Led Development. The World Bank, Washington, DC. http://dx.doi.org/10.1596/978-0-82138480-0. Bast, E., Kretzmann, S., Krishnaswamy, S. and Romine, T. (2012). Low Hanging Fruit: Fossil Fuel Subsidies, Climate Finance, and Sustainable Development. Oil Change International, Heinrich Böll Stiftung North America. http://www.iisd.org/gsi/sites/default/files/g20lib_oilchange_2012_lowhangingfruit.pdf. Bjorvatn, K., Farzanegan, M. R. and Schneider, F. (2012). Resource Curse and Power Balance: Evidence from Oil-Rich Countries. World Development, 40(7). 1308–16. DOI:10.1016/j.worlddev.2012.03.003. CDP (2013). Use of Internal Carbon Price by Companies as Incentive and Strategic Planning Tool: A Review of Findings from CDP 2013 Disclosure. CDP North America white paper. New York. Collier, P. and Venables, A. J. (2013). Closing Coal: Economic and Moral Incentives. Preliminary version, September 2013. Blavatnik School of Government and Department of Economics, University of Oxford, Oxford, UK. Davidsen, C. and Kiff, L. (2013). Ecuador’s Yasuní-ITT Initiative and New Green Efforts-Away from Petroleum Dependency? Occasional Papers, Vol. 3, Issue 1. Latin American Research Centre, University of Calgary. http://larc.ucalgary.ca/sites/larc.ucalgary.ca.new/files/occasionalpapers/ davidsen_kiff_yasuni-itt_ecuador_vol3iss1.pdf. Edenhofer, O. and Kalkuhl, M. (2011). When do increasing carbon taxes accelerate global warming? A note on the green paradox. Energy Policy, 39(4). 2208–12. Erickson, P. and Lazarus, M. (2013a). Accounting for Greenhouse Gas Emissions Associated with the Supply of Fossil Fuels. SEI discussion brief. Stockholm Environment Institute, Seattle, WA, US. http://www. sei-international.org/publications?pid=2419. Erickson, P. and Lazarus, M. (2013b). Assessing the Greenhouse Gas Emissions Impact of New Fossil Fuel Infrastructure. SEI discussion brief. Stockholm Environment Institute, Seattle, WA, US. http://www. sei-international.org/publications?pid=2384. Finer, M., Moncel, R. and Jenkins, C. N. (2010). Leaving the Oil Under the Amazon: Ecuador’s Yasuní-ITT Initiative. Biotropica, 42(1). 63–66. DOI:10.1111/j.1744-7429.2009.00587.x. Frankel, J. A. (2010). The Natural Resource Curse: A Survey. National Bureau of Economic Research. http://www.nber.org/papers/w15836. Friedrichs, J. and Inderwildi, O. R. (2013). The carbon curse: Are fuel rich countries doomed to high CO2 intensities? Energy Policy, 62. 1356–65. DOI:10.1016/j.enpol.2013.07.076. GEA (2012). Global Energy Assessment - Toward a Sustainable Future. Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA and the International Institute for Applied Systems Analysis, Laxenburg, Austria. Goldman Sachs (2013). The Window for Thermal Coal Investment Is Closing. Rocks & Ores. Available at http://thinkprogress.org/wp-content/ uploads/2013/08/GS_Rocks__Ores_-_Thermal_Coal_July_2013.pdf. Grafton, R. Q., Pittock, J., Davis, R., Williams, J., Fu, G., et al. (2012). Global insights into water resources, climate change and governance. Nature Climate Change, 3(4). 315–21. DOI:10.1038/nclimate1746. IEA (2013b). Redrawing the Energy-Climate Map. World Energy Outlook Special Report. International Energy Agency, Paris. http://www.worldenergyoutlook.org/energyclimatemap/. IEA (2013c). World Energy Outlook 2013. International Energy Agency, Paris. http://www.worldenergyoutlook.org/publications/weo-2013/. IPCC (2013). Climate Change 2013: The Physical Science Basis – Summary for Policymakers. Contribution of Working Group I to the Intergovernmental Panel on Climate Change Fifth Assessment Report, Stockholm, Sweden. http://www.climatechange2013.org. Leaton, J., Ranger, N., Ward, B., Sussams, L. and Brown, M. (2013). Unburnable Carbon 2013: Wasted Capital and Stranded Assets. Carbon Tracker and Grantham Research Institute on Climate Change and the Environment, London School of Economics, London. http://www.carbontracker.org/wastedcapital. Meindertsma, W. and Blok, K. (2012). Effects of New Fossil Fuel Developments on the Possibilities of Meeting 2°C Scenarios. Ecofys, Utrecht, Netherlands. http://www.ecofys.com/en/publication/climate-impact-ofnew-fossil-fuel-developments/. Rystad Energy (2013). Petroleum Production under the Two Degree Scenario (2DS). http://www.rystadenergy.com/Downloads/PressReleases/2013Rystad-Energy-Climate-report-Norwegian-Ministry-of-the-environment. pdf. © Tanenhaus / Flickr Sachs, J. D. and Warner, A. M. (2001). The curse of natural resources. European Economic Review, 45(4–6). 827–38. DOI:10.1016/S00142921(01)00125-8. El Cerrejón open-pit coal mine in La Guajira, Colombia, which is connected to a shipping port by a 150km rail line. Gurría, A. (2013). The climate challenge: Achieving zero emissions. Lecture by the OECD Secretary-General, London, 9 October 2013. http://www. oecd.org/about/secretary-general/the-climate-challenge-achieving-zeroemissions.htm. Harstad, B. (2012). Buy Coal! A Case for Supply-Side Environmental Policy. Journal of Political Economy, 120(1). 77 – 115. DOI:10.1086/665405. HSBC (2012). Coal and Carbon: Stranded Assets: Assessing the Risk. HSBC Global Research, London. https://www.research.hsbc.com/midas/ Res/RDV?p=pdf&key=dXwE9bC8qs&n=333473.PDF. HSBC (2013). Oil & carbon revisited: Value at risk from ‘unburnable’ reserves. Hsueh, M. and Lewis, M. C. (2013). Thermal Coal: Coal At A Crossroads. Commodities Special Report. Deutsche Bank Markets Research. IEA (2012a). Medium-Term Coal Market Report 2011 – Market Trends and Projections to 2016. International Energy Agency, Paris. http://www.iea. org/publications/freepublications/publication/name,34731,en.html. IEA (2012b). Medium-Term Coal Market Report 2012 – Market Trends and Projections to 2017. International Energy Agency, Paris. http://www.iea. org/publications/medium-termreports/#coal. IEA (2012c). World Energy Outlook 2012. International Energy Agency, Paris. http://www.worldenergyoutlook.org. IEA (2013a). Key World Energy Statistics 2013. International Energy Agency, Paris. http://www.iea.org/publications/freepublications/publication/key-world-energy-statistics-2013.html. This discussion brief was written by Michael Lazarus and Kevin Tempest, of SEI’s U.S. Centre in Seattle, WA. It is part of a project financed through SEI programme support from the Swedish International Development Cooperation Agency, Sida. Sida does not necessarily share the views expressed in this material. Responsibility for its contents rests entirely with the authors. Sierra Club (2011). Move Beyond Coal, Now! Voices from the Front Lines of the Global Struggle. Washington, DC. http://www.sierraclub.org/coal/ narratives/. Sierra Club (2012). Move Beyond Coal, Now! Victories on the Front Lines. Washington, DC. http://www.sierraclub.org/international/beyondcoalvictories/. Sinn, H.-W. (2009). The Green Paradox. CESifo Forum, 10(3). http://www. cesifo-group.de/portal/pls/portal/docs/1/1191478.PDF#page=12. Sinn, H.-W. (2012). The Green Paradox: A Supply-Side Approach to Global Warming. The MIT Press. U.S. EIA (2013). International Energy Outlook 2013. U.S. Energy Information Administration, Washington, DC. http://www.eia.gov/forecasts/ieo/. Van der Ploeg, F. (2011). Natural Resources: Curse or Blessing? Journal of Economic Literature, 49(2). 366–420. DOI:10.1257/jel.49.2.366. Van der Ploeg, F. and Withagen, C. (2013). Green Growth, Green Paradox and the global economic crisis. Environmental Innovation and Societal Transitions, 6. 116–19. DOI:10.1016/j.eist.2012.11.003. Water in the West (2013). Water and Energy Nexus: A Literature Review. Stanford Woods Institute. http://waterinthewest.stanford.edu/sites/default/ files/Water-Energy_Lit_Review.pdf. Published by: Stockholm Environment Institute Linnégatan 87D, Box 24218 104 51 Stockholm Sweden Tel: +46 8 30 80 44 Author contact: Michael Lazarus, [email protected] Media contact: Marion Davis, SEI Communications [email protected] sei-international.org 2014 Twitter: @SEIresearch, @SEIclimate