Project no. GOCE-CT-2003-505539 Project acronym: ENSEMBLES Project title: ENSEMBLE-based Predictions of Climate Changes and their Impacts Instrument: Integrated Project Thematic Priority: Global Change and Ecosystems D7.1b Critical assessment of the IPCC SRES scenarios Due date of milestone: Actual submission date: March 2005 Start date of project: 1 September 2004 Duration: 60 Months Vn1.0 Project co-funded by the European Commission within the Sixth Framework Programme (2002-2006) PU PP RE CO Dissemination Level Public Restricted to other programme participants (including the Commission Services) Restricted to a group specified by the consortium (including the Commission Services) Confidential, only for members of the Consortium (including the Commission Services) A CRITICAL ASSESSMENT OF THE IPCC SRES SCENARIOS Richard S.J. Tol, Brian O’Neill, Detlef P. van Vuuren March 14, 2005 1. Introduction Emissions scenarios are a crucial part of climate change research. Emissions scenarios are derived from population, economic and technology scenarios, which also shape vulnerability to and hence impacts of climate change. Emissions scenarios drive scenarios of climate change, which in turn drive impacts research. The Intergovernmental Panel on Climate Change (IPCC) Special Report on Emissions Scenarios (SRES) developed a set of scenarios, which currently form the core of most climate change research. This paper critically assesses the SRES, as currently analysed with General Circulation Models (GCMs), including those in the ENSEMBLES Integrated Project. The IPCC SRES scenarios have been used extensively since their publication, and a considerable amount of this work was evaluated in IPCC’s Third Assessment Report (Houghton et al., 2001; McCarthy et al., 2001; Metz et al., 2001). This included research into possible climatic change by climate modelers, impact and adaptation studies and analysis of potential mitigation policies for climate change. The SRES scenarios will also serve as the basis for many of the impact studies to be assessed in the IPCC Fourth Assessment Report now underway. Interestingly, the SRES scenarios have also served as a basis or inspiration for numerous other exercises at global, regional and national levels – where often new modelling was consistent with the overall SRES storylines and published parameters (UNEP, 2002;De Mooij and Tang, 2003; Kainuma et al., 2003; Van Vuuren et al., 2003). The paper is structured as follows. In Section 2, we give a brief overview of how the SRES scenarios came to be, what they are, and what they are not. In Section 3, we contrast scenarios and observations. In Section 4, we critically look at the population scenarios considered. In Section 5, we consider the recent discussion on purchasing power parity versus market exchange rates. In Section 6, we discuss the assumptions of unconditional convergence embedded in the SRES scenarios. Section 7 concludes. 2. A brief overview of SRES In 2000, the IPCC published a new set of emission scenarios in the Special Report on Emission Scenarios (SRES), designed to serve as a basis for assessments of climate change and possible response strategies (Nakicenovic, 2000). The SRES scenarios were developed in a relatively open process that started in 1996. Modelling groups and individuals were invited to contribute to the scenario development. Six modelling teams accepted this invitation and participated in this exercise.1 The IPCC scenarios cover very long time periods (1990-2100) so as to capture the large inertia involved in the climate system. Uncertainties obviously play a major role over such a long time period. Future greenhouse gas emissions result from complex dynamic processes, 1 In addition, draft results of the modelling groups were put on a website for comments by outside reviewers. The scenarios were also reviewed by both experts and government representatives. including demographic and socio-economic development, and technological change. The future evolution of these factors is highly uncertain, with various development patterns capable of introducing very different futures. For example, the question of whether innovation will drive the cost of non-emitting energy technologies down to a level below that of fossil fuels is crucial. The SRES process addressed uncertainty in two ways. First, the scenarios were based on a set of storylines describing alternative broad development patterns. Each storyline was intended to represent consistent demographic, social, economic, technological, and environmental developments. Thus, in contrast to earlier IPCC scenarios, the new scenarios described not only plausible greenhouse gas emission trajectories, but also consistent trajectories of human activities (‘drivers’). Second, the SRES process included six different models for creating quantitative interpretations of each of the storylines. The multimodel approach was intended to capture uncertainties related to model structure. There are four base scenarios: A1, A2, B1, and B2. The A scenarios place more emphasis on economic growth, the B scenarios on environmental protection; the 1 scenarios assume more globalisation, the 2 scenarios more regionalisation. The A1 scenario has three variants, A1(B), A1FI, and A1T. Population growth is highest in A2 (15 billion people in 2100), followed by B2 (10 billion) and A1 and B1 (7 billion). Economic growth is most rapid in the A1 scenario, followed by B1, B2 and A2. All four scenarios assume that developing countries grow faster than developed ones; the gap between rich and poor closes most rapidly in the A1 scenario, followed by B1, B2 and A2. Energy intensity falls in all four scenarios, most rapidly in the B1 scenario, followed by A1, B2 and A2. Coal as an energy source is almost phased out in B1, A1B and A1T, roughly constant (as a share in total energy supply) in A1FI and B2, and increasing in A2. Annual arbon dioxide emissions from fossil fuel combustion reach 30 GtC in the A1FI scenario, 29 GtC in A2, 14 GtC in B2, 13 GtC in A1, 5 GtC in B1 and 4 GtC in A1T in 2100. Carbon dioxide emissions from land use range from 0 to –2 GtC in 2100, equalizing the differences between A1FI and A2, between A1B and B2, and between A1T and B1. Sulphur emissions fall in all scenarios, fastest in A1T and slowest in A2. Methane and nitrous oxide emissions rise in some scenarios (A1F1, A2, B2) but fall in others (A1B, A1T, B1); A1FI has the highest emissions, B1 (for methane) and A1T (for nitrous oxide) the lowest. Emissions of other greenhouse gas increase in all scenarios, except for B1, where they are roughly constant. Precursors follow the same pattern as methane and nitrous oxide. 3. Scenarios and observations Although the SRES scenarios were published in 2000, most models used to develop the scenarios were calibrated on 1990 and 1995 data, and most of the calculations were done well before 1999 (when the review process started). Actual developments through 2000 were obviously not known at that time. Now, information has become available that can be compared against the SRES scenarios. First, the SRES report includes scenario data for both 1990 and 2000, allowing a factual comparison against new data for these time periods. Second, since the publication of SRES, new projections have been published by different sources. These new outlooks can be expected to include the latest (scientific) knowledge and insights into events that have occurred since the development of SRES. They can also be used to judge if these events could have substantially changed possible future trends. Such outlooks often focus on shorter time frames than SRES (20-30 years instead of 100 years). In some cases, however, new long-term scenarios have been published. Van Vuuren and O’Neill (submitted) investigate the consistency of the IPCC SRES scenarios (which start in 1990) in comparison with available 1990-2000 data and recent projections, primarily short-term outlooks. The most important inconsistencies are summarized in Table 7. In almost all the cases of (now) historical development through to and including the 21st century, the SRES assumptions for 1990 and 2000 are reasonably consistent with available data. This certainly holds for the global projections for income, population, energy and nonCO2 gases. Only small differences were found for these variables on the regional scale, in particular, for income trends and energy trends in Asia and REF. For CO2 emissions, the SRES scenarios indicate a slightly more rapid global increase between 1990 and 2000 than is now apparent from emission inventories (15% versus an average of 11%), but the difference in terms of absolute emissions in 2000 is small (mostly caused by the decline in coal use in the late 1990s in China). Finally, for sulfur emissions, there seems to be a clear difference between the assumed change in SRES in the 1990-2000 period and the trend in current inventories (a global 3% versus 20% decline, respectively), mostly resulting from diverging trends in the Asia and REF regions. In both the case of CO2 and sulfur is should be noted trends in China in the late 1990s are not fully known. Comparing the SRES scenarios to current near-term projections shows the SRES scenarios in most cases to be within the range of these projections, both globally and for individual regions. It should also be noted, however, that the range of population and economic projections has shifted downward since SRES publication. While assumptions regarding these drivers in most SRES scenarios still fall within this range, in a few cases, SRES assumptions rise above it. In addition, the low end of the current range is under-represented in the SRES scenarios for both population and economic growth. Revisions of the SRES scenarios based on the same storylines could therefore be based on somewhat lower population projections and near-term economic projections. This would be more important in particularly regions and scenarios. In the case of economic growth, assumptions for the ALM region, the A1 scenario in particular, deserve the most attention. In the case of population, the assumptions for the Asia and ALM regions in the A2 scenario would be the most important to consider for revision since they differ the most from the updated range of projections. In addition, our results show the differences between SRES and more recent population projections for the medium term (2050) to be magnified in the long term (2100) due to the path dependency of population growth. Lower population pathways are likely to lead to slightly lower greenhouse gas emissions, in particular for A1 and B1. For economic growth, this relationship is somewhat less direct, as downward revisions of economic growth in the ALM region might have consequences for technology development and possibilities for important in this region. At the same time, it should be noted that except for the first two decades for A1 – in terms of emissions the SRES scenarios still seem to be fully consistent with the current range of more recent outlooks. This might imply that along with revisions in driving forces, also revisions might be made in the relationship between these drivers and greenhouse gas emissions. Comparison on the regional scale shows that the most important differences between SRES and the current near-term projections occur for the ALM region. Here, the range of SRES economic growth assumptions and resulting growth rates for energy use and CO2 emissions are near the upper end of current projections or beyond. By now, the assumed rapid change in conditions for economic growth in this region seem to have become (even more) questionable. The impact of this region on the global emissions projections is limited. Although to a much smaller degree, the GDP and emissions growth rates of the Asia region in the A1 scenario are also high compared to the recent projections. Another important difference between the SRES scenarios and more recent insights globally occurs for sulfur. As a result of the rapid decline in the 1990-2000 period and expectation about desulfurization policies in low-income countries, a rapid increase in sulfur emissions of some of the SRES scenarios for sulfur between 2000 and 2030 has become very unlikely. Despite the fact that the exact trend in Chinese emissions during the 1990s remains an important uncertainty, a revision of scenarios is likely to result in lower sulfur emissions. It should be noted that this, other factors being equal, implies an increase in the expected temperature change associated with the SRES scenarios. Finally, there are a few elements that have not been included in the SRES scenarios in much detail – and which recently have become much more important for climate change projections; one of these is the emissions of black and organic carbon, while another is gridbased land-use projections. Non-official projections consistent with SRES assumptions have now become available from individual modelling teams. Regarding the question of whether the SRES scenarios have become outdated or not, there are obviously no hard criteria. With a few exceptions, the study reported here has shown the assumed SRES trends to still be plausible. In addition, there is no evidence that underlying axioms of the storylines have been falsified. As a result, at this point in time there seems to be no need for a large-scale IPCC-led update of the SRES scenarios on the sole basis of their performance in the 1990-2000 period, or on the comparison with more recent projections. At the same time, however, individual modelling groups could decide to update their scenarios, making them fully consistent with current trends, while still preserving the connection with the SRES storylines and harmonization criteria. Such an approach has been taken, for instance, by the IMAGE group when it published its detailed elaboration of the SRES scenarios in 2001. Variants of SRES scenarios could also be developed by independent research teams to cover parts of the range of drivers or outcomes that are less well represented in SRES; the low end of the range of future population size is one example. In fact, the SRES report itself allowed for a great diversity of elaboration of the same scenarios – indicating particular criteria for scenarios to meet in order to maintain consistency. Most of these criteria are formulated for the longer term (first criteria to be applied in 2025). The option of updating SRES scenarios (by individual modeling groups), while upholding the connection with the SRES storylines and criteria, will, in general, keep results compatible with earlier work. This will be based on SRES and allow for more comparability (and easier communication) in assessment, for instance, in IPCC’s Fourth Assessment Report. At the same time, the SRES updating option will allow research groups to produce long-term scenarios that are also well suited to shorter term applications.Table 1. Main inconsistencies found between the SRES scenarios and more recent scenarios and data Parameter Population GDP Energy CO2 Non-CO2 gasses Sulfur 4. Population Inconsistencies noted in comparison SRES does not include a representation of the current low-end population scenarios The A2 scenarios outside the current 95% probability estimate For specific regions (in particular sub-Sahara Africa and China), differences between SRES and current projections larger. Global economic projection for A1 is outside range of current projections in the first 2 decades For the ALM region, the set of SRES scenarios seem to be representative of the upper end scenarios only. No major anomalies with historical data See GDP See GDP for short-term projections Slightly too high for 2000 emissions Historically seen, somewhat too high for the F-gases Several forcing agents (black carbon) not included yet 2000 sulfur emissions too high. Emissions in the first decades of the high emission scenarios unlikely The population projections used in SRES were consistent with the demographic outlook at that time (Gaffin, 1998). The projection used in the B2 scenarios was the UN medium variant (UN, 1998). The A1 and B1 scenarios all shared a common, relatively low, population projection from IIASA, while the A2 scenario used a relatively high population projection from IIASA (Lutz et al., 1996). These two projections spanned, at the global level, approximately the 90% uncertainty interval associated with the IIASA probabilistic projections (i.e. a level just within the 5th and 95th percentiles of the distribution). Updated projections, however, generally anticipate less global population growth than the projections used in the SRES scenarios. Since the early 1990s, birthrates in many parts of the world have fallen surprisingly fast and the AIDS epidemic has taken an unexpectedly large toll. These changes have led demographers to revise their outlook on future population downward, toward smaller, older populations than previously anticipated. For example, Figure 1a compares the projections for 2050 used in SRES to the most recent IIASA (Lutz et al., 2001), UN (2003), World Bank (2003) and the US Census Bureau (US.BoC, 2003) projections for the world and the four SRES macro regions. For comparability, the figure plots all population sizes relative to the projected population in the SRES B2 scenario for each region (i.e. the UN medium scenario produced in 1996). For the world as a whole, population was projected at 9.4 billion in 2050 in the SRES B2 scenario. This figure shows that the A2 scenario anticipated a 21% larger global population, and the A1 and B1 scenarios, a 7% smaller population than the B2 scenario. When these scenarios are compared to more recent projections for the world, a small downward revision to the medium (or “best guess”) projections and to the high end of the uncertainty range is shown, along with a relatively large downward revision to the low end of the uncertainty range. As a group, updated medium projections foresee a 3-6% (0.3 to 0.6 billion people) smaller global population in 2050 relative to the SRES B2 projection; similarly, the high end of the range has shifted down, so that the SRES A2 scenario now no longer falls within the 90% uncertainty interval. Rather, it falls 6-7 percentage points (0.5 – 0.7 billion people) above the updated UN high scenario and the 95th percentile of the IIASA uncertainty range. At the low end of the range changes are much larger: the SRES A1/B1 assumptions fall 14-18 percentage points (1.3 – 1.7 billion people) above the UN low scenario and the 5th percentile of the IIASA uncertainty range. Considering the four SRES macro regions, Asia and ALM are shown – due to their very large absolute sizes - to drive the global results. They also share a similar pattern of change (large downward revision to the low end of the uncertainty range and a smaller revision to medium and high end). Analysis of smaller sub-regions (not shown) indicates that these changes are primarily due to changes in the outlook for Sub-Saharan Africa, the Middle East and North Africa region, and the East Asia region. Recent data showing lower than expected fertility in these regions has led to less projected population growth. In addition, a much more pessimistic view on the extent and duration of the HIV/AIDS crisis in sub-Saharan Africa has also lowered anticipated growth in that region. Changes in the outlook in the industrialized countries differ substantially from the global pattern. In the OECD region, the UN projections are actually about 10% higher than previously, despite continuing low fertility in these regions, due mainly to changes in assumptions regarding migration. Previous UN projections did not attempt to project migration beyond 2025, assuming instead that it was zero afterwards; the updated projections assume non-zero migration through 2050. Updated IIASA projections are also slightly higher in this region, due mainly to a more optimistic projection of future life expectancy. In the REF region, projections from both institutions have been revised downward, especially in the UN projections and for the high end of the uncertainty range. These changes have been driven by recent data showing very low fertility levels and mortality that is quite high relative to other industrialized countries, particularly in the Former Soviet Union. It should be noted that the SRES A1/B1 assumptions for the industrialized countries (OECD and REF regions) cannot be directly compared to the low-end range of more recent scenarios, because SRES did not assume a low population growth projection for these regions (even though growth was relatively low in A1/B1 for the world as a whole). Rather, SRES assumed a medium fertility scenario coupled with relatively low mortality in these regions, which in combination resulted in a future growth in these regions that was actually somewhat high relative to a “best guess” projection. Because population growth is a path-dependent process, changes in the estimates for the base year and in the short-term outlook can have important implications for the plausibility of long-term population growth paths. Therefore it is worth comparing the SRES population assumptions to updated projections for the end of the century. IIASA and the UN are the only institutions that have produced updated projections for the world that extend to 2100, shown in comparison to the SRES assumptions in Figure 1b. Patterns are qualitatively similar to those found for 2050, but larger in magnitude: a general downward shift in the full range of projections that is somewhat larger at the lower end. For example, the most recent central projections for global population are 13-19% (1.4-2.0 billion people) lower than the medium population scenario used in the SRES B2 scenarios. Similarly, the SRES A2 population assumption of 15 billion in 2100 is now 10-16 percentage points (1.1 – 1.7 billion) above the UN high and IIASA 95th percentile. At the low end differences are larger: the UN low and IIASA 5th percentile are 15-22 percentage points (1.6 – 2.2 billion) below the SRES A1/B1 assumptions. As was the case with the outlook for 2050, the long term changes at the global level are driven by the developing country regions (Asia and ALM), with the changes particularly large in the China region, Middle East and North Africa, and Sub-Saharan Africa. Although the range of projected population sizes has shifted down since the development of the SRES scenarios, this does not automatically imply that the SRES population assumptions are no longer credible. For example, the assumptions used in the SRES B2 and A1/B1 scenarios still fall within the plausible range of population outcomes according to more recent outlooks (see Fig. 1). What is clearly missing, however, in the current SRES set is a representation of a population projection that is representative of the lowest end of the current range of population projections. This implies that if new scenarios were to be developed today it would make sense to choose lower population growth assumptions, and for this reason some researchers have produced revised versions of the SRES population assumptions. For example Hilderink (2004) provides an alternative interpretation of the demographic implications of the SRES storylines, and produces four new global population projections that span a range of 8 to 12 billion in 2100 (as compared to 7 to 15 billion in SRES). At the high end of the range, the comparison of SRES to the updated outlook is less favourable. The population projection used in the A2 scenarios now falls above the 95th percentile in the IIASA projections and above the most recent UN high scenario. In particular regions, the differences are especially large such as East Asia, Middle East, North Africa and the Former Soviet Union. In these particular regions, the SRES assumptions now strain credibility. Researchers using the SRES population scenarios should take these differences into consideration. It is advisable to use revised projections for the regions with the largest differences if possible. For example, IIASA has recently produced a new population scenario for use in a stabilization variant of an A2 storyline that results in a population of about 12 billion in 2100. It should also be kept in mind that while in the few regions discussed above there is a clear inconsistency between the SRES A2 population assumptions and the more recent outlook, there is, in general, a substantial range of population outcomes that is consistent with any given SRES storyline (O’Neill, 2004). As long as there is consistency between the population assumptions used to generate emissions and to evaluate impacts, researchers need not feel tightly bound to a single population projection for each storyline. (a) Ratios to SRES Medium: World and SRES 4 Regions in 2100 1.4 SRES A2 1.2 Ratio to SRES B2 SRES B2 1.0 SRES A1/B1 0.8 0.6 0.4 UN Low & IIASA 90% uncertainty interval (lower bound) 0.2 UN/WB/USCB Medium & IIASA Median OECD90 REF UN 2003 USBC 2003 & WB 2003 IIASA 2001 SRES USBC 2003 & WB 2003 UN 2003 SRES ASIA IIASA 2001 USBC 2003 & WB 2003 UN 2003 IIASA 2001 SRES USBC 2003 & WB 2003 UN 2003 SRES WORLD IIASA 2001 USBC 2003 & WB 2003 UN 2003 IIASA 2001 SRES 0.0 UN High & IIASA 90% uncertainty interval (upper bound) USBC 2003 WB 2003 ALM Ratios to SRES Medium: World and SRES 4 Regions in 2100 (b) 2.0 SRES A2 1.8 1.6 SRES B2 Ratio to SRES B2 1.4 1.2 SRES A1/B1 1.0 0.8 UN Low & IIASA 90% uncertainty interval (lower bound) 0.6 UN Medium & IIASA Median 0.4 0.2 WORLD OECD90 ASIA REF UN 2003 IIASA 2001 SRES UN 2003 IIASA 2001 SRES UN 2003 IIASA 2001 SRES UN 2003 IIASA 2001 SRES UN 2003 IIASA 2001 SRES 0.0 UN High & IIASA 90% uncertainty interval (upper bound) ALM Figure 1: Population size worldwide and for four SRES macro regions, relative to the population size in the SRES B2 projection for (a) 2050 and (b) 2100. Source: (Nakicenovic and Swart, 2000;Lutz et al., 2001;UN, 2003;US.BoC, 2003;WorldBank, 2003) 5. Exchange rates Recently, the IPCC SRES scenarios have been severely criticised (Castles and Hendersen, 2003a,b; Castles, 2004). The data underlying the SRES scenarios are largely based on market exchange rates (MER) for converting national currencies into US dollars. Castles and Henderson argue that the appropriate conversion should be based on purchasing power parity exchange rates2 (PPP). Under PPP, the gap between rich and poor countries is smaller. Castles and Henderson argue that therefore the economic growth rate and hence the emissions growth rate would have been smaller had the SRES scenarios been based on PPP. Climate change would be much less of a problem. This conclusion and the ensuing debate, commenced by the defensive attitude of the IPCC (IPCC, 2003; Nakicenovic et al., 2003; Grübler et al., 2004), attracted the attention of climate change policy makers, the press (Economist, 2003a,b, 2004), and the sceptics (Michaels, 2003). Per capita income in poor countries tends to be higher when measured in PPP (or RER) than when measured in MER. Castles and Henderson (2003a,b) deduce from this that developing country growth in the future would be slower under PPP than under MER. This implicitly assumes convergence of per capita income (see Section 6). The SRES scenarios and most economic models used for climate change policy analysis indeed assume convergence, so the critique by Castles and Henderson is valid. Besides convergence of per capita income, the SRES scenarios also assume convergence of emissions intensities. Castles and Henderson (2003a,b) overlook this, but as Holtsmark and Alfsen (2004a,b, 2005) and Tol (submitted) point out, switching from MER to PPP exchange rates would increase emission projections, at least partially offsetting the drop in emissions due to the income effect. Manne and Richels (2004) and Manne et al. (forthcoming) use the MERGE model to show that the choice between PPP and MER indeed alters carbon dioxide emissions, but that the differences are small compared to other uncertainties, and that the differences get smaller if one moves from emissions to concentrations to temperatures. Holtsmark and Alfsen (2004a,b, 2005) and Tol (submitted) concur. Tol (submitted) adds that the drop in global carbon dioxide emissions when switching from MER to PPP is entirely due to a drop in emissions from developing countries. This would change the political debate. Moreover, it would also imply a different pattern of SO2 emissions. This effect has yet to be quantified. 6. Convergence The discussion on the exchange rate used highlights the SRES assumptions about the convergence of per capita income and emission intensities. In the economic growth literature (Barro and Sala-i-Martin, 1995), absolute or σ-convergence of per capita income means that poorer countries grow faster than do richer countries. It does not mean that the income gap between rich and poor would be closed by a specific date (e.g., 2100), only that it would tend to fall and would close eventually. Absolute convergence would occur because, if all else is equal, investments in poorer countries would yield a higher return. Unsurprisingly, empirical studies have convincingly demonstrated that all else is not equal, and absolute convergence has not happened. Conditional, club or β-convergence is 2 Strictly speaking, PPP exchange rates are not exchange rates in the sense that one can swap currencies at this rate; rather, PPP “exchange rates” are measures of cross-country differences in price levels. observed, however. Here, similar countries converge to the same income level. The clubs may diverge, however. Each of the SRES scenarios assume absolute convergence of per capita incomes (Nakicenovic and Swart, 2000). Miketa and Mulder (forthcoming) test the convergence assumption in energy intensities. They find weak evidence for absolute convergence in the amount of energy used per dollar of income generated, but strong evidence for conditional convergence. Each of the SRES scenarios assume absolute convergence of emission intensities (Nakicenovic and Swart, 2000). As with PPP v MER, the erroneous assumption on convergence of emission intensities at least partly offsets the erroneous assumption on convergence of per capita incomes. Again, the implication would be slower economic growth in developing countries, and slightly slower growth in their emissions. This would more pronounced in regional emissions of greenhouse gases and aerosols than in global emissions, less pronounced in greenhouse gas concentrations, and even less in the global mean temperature and sea level. 7. Conclusions The IPCC SRES emissions scenarios leave much to be desired. However, they constitute the standard scenarios, and their quality is not worse, and often better than alternative emissions scenarios. Moreover, much of the critique is directed at the demographic and economic details of the scenarios. This may have lead to a small upward bias of emissions projection. The range of future greenhouse gas emissions is undisputed, however. It is therefore appropriate that the ENSEMBLES GCMs run the SRES scenarios. Acknowledgements The authors thank the comments received from Philip Bagnoli, Arnulf Grübler, David Henderson, Jean-Charles Hourcade, Tom Kram, Keywan Riahi, Roberto Roson, Bill Nordhaus, Hom Pant, Rich Richels, Jim Sweeney, Bert de Vries and John Weyant for their comments contributed in various production stages of this paper. The CEC DG Research through the NEMESIS/ETC and ENSEMBLES projects (ENG2-CT01-000538; GOCE-CT2003-505539) and the Michael Otto Foundation for Environmental Protection provided welcome financial support. References Barro, R. J. and Sala-i-Martin, X. (1995), Economic Growth MIT Press, Cambridge. Castles, I. (2004), ‘Climate Work Based on Unsound Economics’, Australian Financial Review (Feb 7th). Castles, I. and D. Henderson (2003a), ‘The IPCC Emission Scenarios: An EconomicStatistical Critique’, Energy and Environment, 14 (2-3), 159-185. Castles, I. and D. Henderson (2003a), ‘Economics, Emission Scenarios and the Work of the IPCC’, Energy and Environment, 14 (4), 415-435. De Mooij, R. and P. Tang (2003), Four Futures of Europe, CPB Netherlands Bureau for Economic Policy Analysis, The Hague, The Netherlands. Economist (2003a), Hot Potato. The Intergovernmental Panel on Climate Change had better check its calculations (Feb 13th). Economist (2003b), Hot Potato Revisited. A Lack-of-Progress Report on the Intergovernmental Panel on Climate Change (Nov 6th). Economist (2004), Measuring Economies: Garbage In, Garbage Out (May 27th). Gaffin, S. R. (1998), 'World population projections for greenhouse gas emissions scenarios', Mitigation and Adapatation Strategies for Global Change, 3, 133-170. Grübler, A., N. Nakicenovic, J. Alcamo, G. Davis, J. Fenhann, B. Hare, S. Mori, B. Pepper, H. Pitcher, K. Riahi, H.-H. Rogner, E. Lebre La Rovere, A. Sankovski, M. Schlesinger, R.P. Shukla, R. Swart, N. Victor and Tae Young Jung (2004), “Emissions Scenarios: A Final Response,” Energy and Environment, vol. 15, No. 1, pp. 11-24. Hilderink: 2004. Holtsmark, B.J. and K.H. Alfsen (2004a), On the Question of PPP Corrections to the SRES Scenarios, Policy Note 2004-01, CICERO, Oslo. Holtsmark, B.J. and Alfsen, K.H. (2004b), ‘The Use of PPP or MER in the Construction of Emission Scenarios is more than a Question of Metrics’, Climate Policy, 4 (2). Holtsmark, B.J. and Alfsen, K.H. (2005), ‘PPP Correction of the IPCC Emission Scenarios – Does It Matter?’, Climatic Change, 68 (1-2),11-29 (also: Discussion Paper 366, Statistics Norway, Oslo). Houghton, J. T., Y. Ding et al. (2001), Climate Change 2001: The Scientific Basis, Cambridge University Press, Cambridge. IPCC (2003), IPCC Press Information on AR4 and Emissions Scenarios (http://www.ipcc.ch/press/pr08122003.htm). Kainuma, M., Y. Matsuoka et al. (2003), 'Application of AIM/Enduse Model to Japan', in Climate Policy Assessment - Asia-Pacific Integrated Modeling, M. Kainuma, Y. Matsuoka and T. Morita (eds.), Springer, Tokyo. Lutz, W., W. Sanderson et al. (1996), 'World population scenarios for the 21st century'. in The Future Population of the World. What Can We Assume Today? W. Lutz. (ed.), Earthscan, London: 361-396. Lutz, W., W. Sanderson et al. (2001), ' The end of world population growth.' Nature, 412: 543-545. Manne, A.S. and R.G. Richels (2003), Market Exchange Rates or Purchasing Power Parity (Does the Choice Make a Difference in the Climate Debate? AEI-Brooking Joint Center for Regulatory Studies Working Paper 03-11 (http://www.aeibrookings.org/admin/authorpdfs/page.php?id=290). Manne, A.S., Richels, R.G. and Edmonds, J.A. (forthcoming), ‘Market Exchange Rates or Purchasing Power Parity: Does the Choice Make a Difference to the Climate Debate?’, Climatic Change. McCathy, J. J., O. F. Canziani et al. (2001), Climate change 2001: Impacts, adaptation, and vulnerability. Cambridge University Press, Cambridge. Michaels, P. (ed.) (2003), ‘Bad Math’, World Climate Report, 13 (10). http://www.co2andclimate.org Miketa, A. and Mulder, P. (forthcoming), ‘Energy-Productivity across Developed and Developing Countries in 10 Manufacturing Sectors: Patterns of Growth and Convergence’, Energy Economics. Metz, B., O. Davidson et al. (2001), Climate Change 2001: Mitigation. Cambridge University Press, Cambridge. Nakicenovic N. and Swart, R.J. (2000) Emissions Scenarios 2000 – Special Report of the Intergovernmental Panel on Climate Change, Cambridge University Press, Cambridge. Nakicenovic, N., Grübler, A., Gaffin, S., Jung, T.T., Kram,T., Morita, T., Pitcher, H., Riahi, K., Schlesinger, M., Shukla, P.R., Van Vuuren, D., Davis, G., Michaelis, L., Swart, R. and Victor, N. (2003), ‘IPCC SRES Revisited: A Response’, Energy and Environment, 14 (2-3), 187-214. O'Neill, B. C. (2004), 'Conditional probabilistic population projections: an application to climate change.' International Statistical Review, 72(2): 167-184. Tol, R.S.J. (submitted), ‘Exchange Rates and Climate Change: An Application of FUND’, Climatic Change. UN (1998), World Population Projections to 2150, United Nations, New York. UN (2003), World Population Prospects - The 2002 Revision, Highlights. United Nations, New York. UNEP (2002), Global Environment Outlook 3, EarthScan, London. US.BoC (2003), International Data Base - updated 17 July 2003. US.Bureau of the Census. Van Vuuren, D. P., Z. Fengqi et al. (2003), 'Energy and emission scenarios for China in the 21st century - exploration of baseline development and mitigation options.' Energy Policy, 31: 369-387. Van Vuuren, D.P. and B. O’Neill (submitted), ‘The consistency of IPCC’s SRES scenarios to 1990-2000 trends and recent projections’. WorldBank (2003), World Development Indicators. Worldbank, Washington DC.