In this article we examine the technological feasibility of the global target of reducing GHG emissions to 50 % of the 1990 level by the year 2050. We also perform a detailed analysis of the contribution of low-carbon technologies to GHG emission reduction over mid- and long-term timeframes, and evaluate the required technological cost. For the analysis we use AIM/Enduse[Global], a techno-economic model for climate change mitigation policy assessment. The results show that a 50 % GHG emission reduction target is technically achievable. Yet achieving the target will require substantial emission mitigation efforts. The GHG emission reduction rate from the reference scenario stands at 23 % in 2020 and 73 % in 2050. The marginal abatement cost to achieve these emission reductions reaches $150/tCO2-eq in 2020 and $600/tCO2-eq in 2050. Renewable energy, fuel switching, and efficiency improvement in power generation account for 45 % of the total GHG emission reduction in 2020. Non-energy sectors, namely, fugitive emission, waste management, agriculture, and F-gases, account for 25 % of the total GHG emission reduction in 2020. CCS, solar power generation, wind power generation, biomass power generation, and biofuel together account for 64 % of the total GHG emission reduction in 2050. Additional investment in GHG abatement technologies for achieving the target reaches US$ 6.0 trillion by 2020 and US$ 73 trillion by 2050. This corresponds to 0.7 and 1.8 % of the world GDP, respectively, in the same periods. Non-Annex I regions account for 55 % of the total additional investment by 2050. In a sectoral breakdown, the power generation and transport sectors account for 56 and 30 % of the total additional investment by 2050, respectively.
Ambitious long-termFootnote 1 climate targets are being seriously considered in international climate policy arenas. Under the Cancun agreements concluded at the 16th session of the Conference of the Parties (COP16), for example, the conference of parties recognizes the long-term climate goal of holding the increase in global average temperature below 2 °C above pre-industrial levels. At the G8 summit held in L’Aquila in 2009, the leaders of the G8 countries agreed to share the goal of achieving at least a 50 % reduction of global emissions by 2050.
Climate change mitigation models have been used to explore GHG emission reduction scenarios. In its Fourth Assessment Report (AR4), the Intergovernmental Panel on Climate Change (IPCC) reviewed 177 emission mitigation scenarios and classified them into six categories based on the stringency of the climate targets (IPCC 2007). According to the classification, the global temperature target of 2 °C and the emission reduction target of 50 % by 2050 correspond to the most stringent category, category I (Table 1).
In the scenarios in category I, CO2 emissions peak in 2000–2015 and drop to −85 to −50 % in 2050 relative to the 2000 level. While these results certainly furnish policymakers with valuable information, one should be mindful of their robustness. The number of scenarios in category I is quite limited, accounting for only 6 out of all 177 scenarios assessed. To make up for this limitation, the modeling community has been actively exploring low climate stabilization scenarios after the AR4. EMF 22, for example, considered the GHG concentration stabilization target of 450 ppm CO2-eq and examined the achievability of this target under different international mitigation policies and emission pathways (Clarke et al. 2009). The ADAM project analyzed the technical feasibility and economic viability of the 2 °C target (Edenhofer et al. 2010). The RECIPE project assessed the achievability of a CO2 concentration target of 450 ppm (a level roughly corresponding to 530–550 ppm CO2-eq) and examined how technology and international policy frameworks influenced this achievability (Luderer et al. 2011). The main objective of these existing studies is to assess the long-term (up to 2100) technical feasibility and economic viability of low stabilization targets from a macroscopic perspective. Detailed assessments of the technologies were therefore outside the scope of the studies. Only a few groups so far have conducted detailed technological assessments in stringent climate target scenarios (IEA 2010, for example). As such, a detailed understanding of technologies within a long-term stringent GHG mitigation scenario is still awaited. A mid-term perspective is also required. According to UNEP (2010), the pledged mid-term emission reductions still fall far below the actual mid-term emission reduction required to meet the long-term climate target of 2 °C. To bridge this gap, a mitigation study needs to describe a mid-term perspective that aligns consistently with the long-term goal.
In this study we use a techno-economic approach to examine the technological feasibility of a global reduction of GHG emissions by 50 % relative to the 1990 level by 2050, a target that roughly corresponds to the climate target of 2 °C. We also perform a detailed analysis of the contribution of low-carbon technologies to GHG emission reduction in the mid- and long-term and evaluate the required technological cost.Footnote 2
The analysis in this paper uses AIM/Enduse[Global], a techno-economic model for mid- to long-term climate change mitigation policy assessment. AIM/Enduse[Global] is a dynamic recursive model with a 1-year time step and a detailed framework for technology selection. The model selects technologies by linear programming algorithms that minimize the total system cost (including the initial investment, operation, and maintenance costs of technologies, energy cost, and other costs such as carbon tax) given fixed service demands such as steel production, passenger transport, space heating demand, etc. The model estimates energy consumption and GHG emissions (e.g., CO2, CH4, N2O, HFC, PFC, and SF6) driven by technological change. Kainuma et al. (2003) provide a detailed formulation of the model.
The version of AIM/Enduse[Global] used in this article splits the world into 32 regions over a time horizon from 2005 to 2050. It covers energy sectors through the phases of energy production to end-use, and non-energy sectors, including agriculture, waste, and F-gases (Fig. 1). Emission from land use change is treated as an exogenous scenario.Footnote 3 A foremost feature of the model is its detailed description of technologies not only in energy supply sectors, but also in energy end-use sectors and non-energy sectors (Table 2).
Future service demands
A necessary step, in implementing AIM/Enduse[Global], is to set future service demands in each service and sector. In this study we project future service demand based on population and GDP scenarios. For the population scenario we apply a UN medium variant (UN 2009) in which the world population reaches 9.2 billion in 2050. For the GDP scenario we assume that the world GDP grows by 2.7 %/year from 2005 to 2050 on average, a rate similar to that in the SRES B2 scenario (Nakicenovich et al. 2000). The use of population and GDP scenarios enables us to project future service demands such as industrial production, transport volume, etc., based on statistical model analyses. Akashi et al. (2011) and Hanaoka et al. (2009) offer detailed descriptions of service demand projections. Table 3 summarizes the socioeconomic scenarios and projected service demands in major regions. Global crude steel production increases by an average of 2.0 %/year between 2005 and 2050, or by 2.4 times throughout the whole period. India has the highest rate of growth and becomes the world’s largest steel producer in 2050. Global cement production in 2050 reaches 2.0 times the production level in 2005. China remains the largest cement producer up to 2050, but India has the highest rate of growth. Passenger and freight transport volume grow by about 2 %/year worldwide on average between 2005 and 2050, and the growth is especially fast in China and India. Industrialized regions have moderate rates of growth in industrial production and transport volume, as a consequence of relatively low rates of economic growth. Industrial production and transport volume decline in the long term in Japan, which has a decreasing population and the lowest rate of economic growth.
Key assumptions on the availability of resources and technologies
The model simulation is subject to assumptions on the availability of energy resources and key technologies. This section describes the model’s assumptions on the availability of renewable energy, nuclear power, and carbon dioxide capture and storage (CCS).
The potential of solar and wind power depends on natural conditions such as insolation, wind, and geography. We evaluate the power generation potentials of solar and wind by conducting a geographically explicit analysis. The detailed methodology for this approach is provided in Masui et al. (2010). The estimated total technical potential, after considering the conversion efficiency and suitability of the land, is 166 PWh for solar and 47 PWh for wind (Fig. 2). The potential is broken into several grades by generation cost. In 2005, the generation cost for solar is much higher than that for wind. The cost of solar drops over time, however, and becomes competitive with that of wind in 2050. This cost reduction derives from reductions in technology costs assumed based on IEA (2010).
The future bioenergy potential is subject to various conditions such as land use, food demand, and agricultural productivity. A number of studies have evaluated the future bioenergy potential. We compare the global technical potential of bioenergy in 2050 estimated by previous studies. The estimated bioenergy potential in 2050 ranges broadly from 0.8 to 8.8 Gtoe at the low end of the scale to 11–35 Gtoe at the high end (Fig. 3). Here we assume a worldwide bioenergy potential of 8.7 Gtoe in 2050, the low-end estimate from Smeets et al. (2007). This value is on the high side of the low-end estimates and lower than the lowest of the high-end estimates (11 Gtoe). Smeets et al. (2007) include three types of bioenergy sources, namely, bioenergy crops, agricultural and forestry residues and waste, and forest growth. Bioenergy crops include only those cultivated from surplus agricultural land gained by increasing efficiency of food production. Thus, according to Smeets et al. (2007), the bioenergy potential of 8.7 Gtoe can be supplied without sacrificing food production or expanding the area of agricultural land. Based on this information, we assume that bioenergy production of less than 8.7 Gtoe causes no major change of land use and no additional CO2 emission.Footnote 4
For nuclear energy, we develop a scenario for future nuclear power capacity expansion based on existing government plans and use it for all model runs. The scenario includes new construction of nuclear power plants already under construction and nuclear power plants already planned or proposed. Information on the new construction of nuclear power plants is taken from the World Nuclear Association (http://www.world-nuclear.org/info/reactors.html). In this scenario, the global total nuclear power plant capacity increases from 364 GW in 2005 to 846 GW in 2050.Footnote 5
For CCS, we assume a worldwide CO2 storage capacity of about 4,600 GtCO2. This is a median of the estimated values in various studies (Dooley et al. 2006; Hendriks et al. 2004; IEA 2008, 2010). Further, we assume the maximum annual storage rate based on an ambitious growth pathway in IEA (2010). In this scenario, the maximum annual CO2 storage worldwide in 2050 is about 10 GtCO2.
GHG price paths
To understand the relationship between GHG emission reduction and the emission reduction cost, we perform multiple model runs with different GHG price paths and compare the resulting emissions. Figure 4 shows 13 GHG price path scenarios run through the model.
The scenario names are based on the GHG price in 2050 (in the s800 scenario, for example, the GHG price in 2050 is $800/tCO2-eq). In all of the scenarios except the s0 scenario, the GHG price starts from $0/tCO2-eq in 2010 and increases linearly up to 2050 (the price in the s0 scenario stays at zero). The plot therefore shows, for example, a GHG price of $200/tCO2-eq in the year 2020 in s800 scenario.
The s0 scenario can be regarded as the ‘no climate policy’ case, as it lacks any incentive to reduce GHG emissions specifically for climate mitigation. Accordingly, we use the s0 scenario as the basis for emission reduction. For convenience, we refer to the s0 scenario as the ‘reference scenario’ in the sections to follow.
Global GHG emissions in the reference scenario reach 52 GtCO2-eq in 2020 and 70 GtCO2-eq in 2050. These levels correspond to a 37 and 85 % increase relative to the 1990 level, respectively (Fig. 5). GHG emissions increase more rapidly in non-Annex I regions than in Annex I regions: the average growth rate for GHG emissions from 1990 to 2050 in the former is 1.5 %/year, while that in the latter is only 0.3 %/year. As a consequence, the share of GHG emissions from non-Annex I regions increases from 49 % in 1990 to 60 % in 2020 and to 65 % in 2050. The share of GHG emissions from Asian regions, that is, from Japan, China, India, and ‘Other Asia,’ also changes remarkably, rising from only 25 % in 1990 to about 40 % in 2020. By country, the GHG emissions grow fast in China and India, reaching 4- and 4.5-fold the 2005 levels by 2050, respectively.
Achievability of the target and required GHG emission reduction
In this section we ask two questions: “Will it be technically possible to achieve a 50 % reduction of GHG emissions by 2050 relative to the 1990 level?” and if so, “What emission reduction will be required in major countries in the mid- and long-term?” We address these questions using marginal abatement cost (MAC) curves.
Developing the MAC curves
A MAC curve depicts the relationship between the MAC and emission reduction in a region and year in question. To develop MAC curves here, we use the simulation results of GHG price path scenarios in which GHG emissions are estimated along an externally fixed GHG emission price path. The GHG emission price in these price scenarios is theoretically equal to a MAC of GHG emission. Hence, we develop the MAC curves using the relationship between the GHG emission price and GHG emission reduction in GHG price path scenarios relative to the reference scenario. Note that GHG emission trading among the regions does not take place in GHG price path scenarios. Therefore, the MAC curves developed in this study represent the relationship between the MAC and GHG emission reduction within the region. Figure 6 illustrates how the MAC curves are developed for this study.
MAC curves are developed in two steps: (1) simulate GHG emissions in each GHG price path scenario (see Fig. 6b), (2) draw the MAC curve by plotting GHG emission change rates (R) and the corresponding carbon prices (P) (see Fig. 6c).
Analysis using MAC curves
Figure 7 shows MAC curves estimated for six major regions and the world in 2020 and 2050.
The MAC curve for each region can be characterized by the x-intercept and slope of the curve. The x-intercept represents the GHG emission change rate relative to 1990 in the reference scenario, in which the GHG price is $0/tCO2-eq. The slope of the curve represents the sensitiveness of GHG emissions to the MAC: the milder the slope, the larger the GHG emission reduction when the MAC increases.
In 2050, MAC curves for China and India have very high x-intercepts and remarkably mild slopes, especially in the lower MAC range. This shows that, in spite of the significant increase in GHG emissions in 2050 relative to 1990 in the reference scenario, there are huge GHG emissions reduction potentials in China and India in the lower range of cost. Among the industrialized regions, the MAC curve for the USA has the mildest slope. At the cost of $800/tCO2-eq, the reduction rate relative to 1990 reaches about 90 % in the USA, whereas those of EU27 and Japan reach about 70 %. The variance of the reduction rate among different regions stems from differences in the reference emissions, technology performance and availability (including renewable energy, CCS), energy and non-energy service demand structures, energy price, etc.
Figure 7 indicates that the GHG emission reduction target of 50 % relative to 1990 is achievable at a marginal cost of $600/tCO2-eq. If we assume the same MAC—$600/tCO2-eq—across the world, GHG emissions in 2050 end up at −85 % in the USA, −66 % in the EU, −70 % in Japan, −13 % in China, and +47% in India, compared to the 1990 level. Next, we want to determine which emission reductions in 2020 are consistent with the 2050 target. According to the GHG price path scenarios, the GHG price of $150/tCO2-eq in 2020 corresponds to the GHG price of $600/tCO2-eq in 2050 (see Fig. 4). Therefore, the reduction rate at $150/tCO2-eq in 2020 is consistent with the 2050 target. At $150/tCO2-eq, global GHG emissions increase by 6 % in 2020 relative to the 1990 level. The changes of regional GHG emissions at $150/tCO2-eq in 2020 relative to 1990 differ significantly among regions: −17 % in the USA, −25 % in the EU27, −12 % in Japan, +99 % in China, and +65 % in India. Note that these values include only domestic GHG emissions and do not include carbon credit, which is traded internationally. Thus, the values do not correspond directly to regional emission targets, as the emission targets might include carbon credit.
Transition scenario for achieving a 50 % reduction by 2050
In this section we present the s600 scenario in which GHG emissions in 2050 are reduced by 50 % relative to the 1990 level, with a focus on dynamic changes in global GHG emissions and energy systems.
GHG emission path
In the s600 scenario, global GHG emissions become 40 GtCO2-eq in 2020 and 19 GtCO2-eq in 2050, values that correspond to +6 and −50 % of the 1990 levels, respectively (Fig. 8). Compared to the reference scenario, a significant GHG emission reduction is required in the s600 scenario: the rates of GHG emission reduction from the reference scenario are 23 % in 2020 and 73 % in 2050. The average annual rate of GHG emission reduction from 2005 to 2050 in the s600 scenario is 1.9 %.
A decomposition analysis will help us understand, from a macroscopic viewpoint, how that rapid emission reduction is achieved in the s600 scenario. This method is based on the Kaya identity (Yamaji et al. 1991). The approach begins with an identity in which CO2 emissions from fossil fuel combustion can be expressed as the product of four terms, as follows:
where CO2 is CO2 emission, PE is primary energy consumption, GDP is gross domestic product, and POP is population. The term CO2/PE represents average carbon intensity of energy, PE/GDP represents economy-wide energy intensity, and GDP/POP represents average per capita GDP.
Figure 9 shows the result of the decomposition.
Population and per capita GDP are the increasing factors. Per capita GDP increases rapidly, reaching 2.4-fold the 2005 level by 2050. In spite of the increasing population and per capita GDP, CO2 emissions decrease because of significant reductions of energy intensity and carbon intensity. Energy intensity is the fastest-declining factor in the coming 3 decades and halves by 2040. Carbon intensity plays a somewhat smaller role than energy intensity in reducing CO2 in the near future. As time passes, however, it plays an increasingly important role, eventually overtaking energy intensity after 2040. By 2050, carbon intensity drops to one-fourth of the 2005 level.
Energy system transitions
This section interprets sectoral results to help us better understand the energy system transitions in a scenario where the targeted 50 % reduction of GHG emissions by 2050 is achieved.
In the reference scenario, global power generation increases from 17 to 47 PWh over the period from 2005 to 2050 (Fig. 10). The energy source composition changes moderately in the reference scenario over the same period. The share of coal, for example, increases from 42 to 51 %. The CO2 emission factor of electricity, namely, CO2 emission per unit of electricity generation, decreases gradually over time, thanks mainly to improved generation efficiency in thermal power plants.
In contrast to the reference scenario, power generation technologies drastically change in the s600 scenario. Coal power generation, the largest contributor to CO2 emission in 2005, contributes progressively less in s600 as time passes, and CCS is introduced after 2020. The deployment of renewable energy accelerates over the same period: wind accelerates after 2010; solar and biomass accelerate after 2020 and 2030, respectively. Thus, the share of renewables dramatically increases over time: by 2050, wind, solar, biomass, and hydro together account for about 75 % of the total power generation. The introduction of bioenergy in combination with CCS,Footnote 6 a power generation technology with a net negative emission, in 2040, confers a significant effect, resulting in a net negative CO2 emission factor from that point forward.
In the reference scenario, energy consumption in the industrial sector in 2050 reaches 2.2-fold the level of 2005 (Fig. 11). The shares of gas and electricity increase in the fuel mix. As a consequence of this increase in energy consumption and change in the fuel mix, direct CO2 emissions in 2050 reach 2.1-fold the level of 2005.
The s600 scenario diverges from the reference case in energy saving and through a fuel switch. The change in energy saving in s600 is derived from reduced fuel consumption: in 2050, energy consumption is reduced by 10 % from the reference case. The fuel shift in the s600 scenario is a large shift from coal to gas. The share of coal declines from 35 to 10 % from 2005 to 2050, while that of gas rises from 17 to 41 %. As a consequence of this energy saving and fuel switch, direct emissions of CO2 in 2050 are reduced by half from the reference scenario, ending up, in 2050, at about the same level as 2005. Moreover, if indirect CO2 emissions by electricity use are included, the significantly improved CO2 emission factor of electricity in the s600 scenario (see Fig. 10c) substantially reduces the CO2 emissions from the reference level. CO2 emissions in 2050 are reduced by 82 % from the reference scenario and by 62 % from the 2005 level, if indirect CO2 emissions are included.
Considerable technological changes take place in the transport sector. Figure 12 shows the technological change in passenger cars. In the reference scenario, the efficient internal combustion engine vehicle (ICEV) becomes widespread. The hybrid electric vehicle (HEV) appears about 15 years into the scenario, from 2020, and steadily grows in prominence until 2050, when its share of total vehicles reaches 30 %.
The technological transition in the s600 scenario is more significant than that in the reference scenario. HEV is introduced on a large scale after 2015, and its share reaches more than 60 % by 2035. The fuel cell vehicle (FCV) is rapidly deployed after 2035, and its share reaches about 45 % in 2050.
As a consequence of the technological changes in the s600 scenario, the total energy consumption of the transport sector is reduced by 25 % from that in the reference scenario in 2050 (Fig. 13). The widespread use of biofuel in s600 also contributes to reduced oil consumption: oil consumption falls by about 20 % by 2050 relative to 2005. This, in turn, results in a significant CO2 emission reduction in the s600 scenario: direct CO2 emission in 2050 is 60 % lower than that in the reference scenario and 17 % lower than the 2005 level. Moreover, if indirect emission is included, CO2 emission in 2050 is reduced by half relative to 2005. The negative emission factor of hydrogen, which is produced from biomass in combination with CCS, contributes largely to the reduction of indirect CO2 emissions.
In the reference scenario, energy consumption in residential and commercial buildings increases by about 60 % by 2050 relative to 2005 (Fig. 14). The energy mix changes considerably over time in the reference scenario, with a marked decrease of biomass and marked increase of electricity. Biomass accounts for about 30 % of total energy use in buildings in 2005, most of which is traditional biomass use in the residential sector. Traditional biomass use declines over time in the reference scenario: by 2050, it accounts for only 7 % of total energy consumption. In contrast to biomass, the consumption of modern forms of energy such as LPG, city gas, and electricity increases. The increase in electricity consumption is the most conspicuous: from 2005 to 2050, the share of electricity in total energy consumption rises from 26 to 47 %. The increased energy consumption, in combination with the fuel mix change, pushes up CO2 emissions substantially in the reference scenario. If indirect emission is included, CO2 emissions in 2050 increase by 88 % relative to 2005.
Energy consumption in the s600 scenario shows no significant divergence from that in the reference scenario, but the drastic improvement in the CO2 emission factor of electricity in the s600 scenario brings about a substantial reduction of CO2 emissions (a 75 % reduction relative to 2005) when indirect emissions are included.
Technologies for achieving 50 % reduction
The “Energy system transitions” section described energy system changes in a scenario where the targeted 50 % reduction of GHG emissions by 2050 is achieved. This section gives a more detailed assessment of the respective contributions of technologies to the GHG reductions in 2020 and 2050.
In the s600 scenario, GHG emissions must be reduced by 12 GtCO2-eq and 51 GtCO2-eq in 2020 and 2050, respectively, relative to the reference scenario. Figure 15 shows the contributions of various technologies to GHG reduction in 2020 and 2050.
In 2020, the power generation sector contributes the most to GHG emission reduction, accounting for 45 % of the total reduction achieved. The renewable energies, namely, solar, wind, and biomass, play a big role, together accounting for 31 % of the total GHG emission reduction. The remaining reduction in the power sector mainly comes from fuel switching and efficiency improvement in thermal power generation. The industrial sector accounts for 12 % of the total GHG reduction in 2020. Among the technologies in the industrial sector, efficient industrial motors make a relatively high contribution to GHG reduction. The transport sector accounts for 10 % of the total GHG emission reduction in 2020. Biofuel contributes the largest reduction in the transport sector. The other reductions in the transport sector are attained from the introduction of the HEV and fuel efficiency improvement of conventional passenger vehicles, trucks, and other transport modes.
Non-energy technologies contribute substantially. In 2020, for example, they account for as much as one-fourth of the total GHG emission reduction. Among the non-energy technologies, systems to control fugitive CH4 emissions, including systems for gas recovery and utilization, contribute a substantial part of the 2020 reductions. Meanwhile, the waste management and agriculture sectors, respectively, contribute up to 6 and 4 % of the total GHG emission reduction in 2020.
In contrast to 2020, non-energy technologies in 2050 contribute less than 10 % of the total GHG reduction. In other words, more than 90 % of the total GHG reduction in 2050 is attained from energy technologies. Among the energy technologies, CCS contributes substantially. CCS systems are installed in power plants, other transformation processes, and energy-intensive industries such as iron and steel and cement. In total, CCS contributes about 100 GtCO2-eq of the GHG emission reduction, or about 20 % of the total reduction, in 2050. Solar power generation, wind power generation, biomass power generation, and biofuel also contribute substantially to the GHG emission reduction. In 2050, for example, they collectively account for 44 % of the total reduction.
Technological cost of achieving a 50 % reduction
A 50 % reduction of GHG emissions by 2050 can be achieved by introducing the technologies described in “Technologies for achieving 50 % reduction.” Yet introducing GHG emission reduction technologies also requires additional cost. Our next task, therefore, is to determine cost for introducing emission reduction technologies in different regions and sectors. In this section we assess the additional investment and total technological cost to achieve the s600 scenario.
In the s600 scenario, worldwide cumulative incremental investment reaches US$ 6.0 trillion by 2020 and US$ 73 trillion by 2050 relative to the reference scenario. These amounts correspond to 0.7 and 1.8 % of world GDP in the same periods.
Figure 16 shows a regional breakdown of required incremental investment cost in the s600 scenario relative to the reference scenario by 2020 and 2050. By 2020, Annex I regions account for about half of total world investment, and non-Annex I regions account for 46 %. Yet by 2050, the share of non-Annex I regions in world investment rises to 55 %. By country, the USA and China together account for a large share: these two countries, together, account for 46 % of the total investment by 2020 and 36 % of the total investment by 2050.
In a sectoral breakdown, the power sector accounts for the largest share, followed by the transport sector (Fig. 17). The power generation and transport sectors account for 59 and 19 % of the total additional investment by 2020, respectively. The large investment in FCV after 2035 pushes up additional investment in the transport sector remarkably, to 30 % by 2050.
Total technological cost
This section assesses the total technological cost. The total technological cost is composed of investment cost and operating cost, the latter of which includes energy cost and maintenance cost. Earlier, in “Investment cost,” we presented quantitative estimates of the investment cost. Thus, our main focus here will be the operating cost and the sum of the investment cost and operating cost.
GHG mitigation technologies may affect the operating cost in two ways, by decreasing it or increasing it. Typical among technologies that decrease the operating cost is energy-saving technology, which lowers the annual energy cost by lowering energy consumption. Typical among technologies that increase operating cost are those that consume extra energy to reduce GHG emissions, such as CCS. Another cause of increased energy cost is fuel switching from low-cost to high-cost fuel: the switch from coal to natural gas, for example, may raise the energy cost.
Figure 18 shows the cumulative technological cost worldwide by 2050 in the s600 scenario relative to the reference scenario.
The two types of effect discussed above lead to different operating cost trends in different sectors. In the power sector, energy-saving, fuel-switching, and the introduction of CCS all take place in the s600 scenario. The mixed effect leads to a decrease in the operating cost by 2050, but only a very small decrease relative to the increase of the investment cost. In the industrial sector, industries make the switch from coal to gas (see Fig. 11) and introduce CCS on a large scale in energy-intensive sectors such as iron, steel, and cement. As a consequence, the operating cost increases at an accelerated pace: by 2050, the additional operating cost is 1.9-fold higher than the additional investment cost. The operating cost in the buildings sector decreases over the long term, but this decrease is rather small relative to the increase of the investment cost.
In contrast, we see a different trend, a significant decrease in the operating cost, in the transport sector. CO2 reduction technologies in transport such as efficient ICEV, HEV, and FCV reduce energy consumption substantially, albeit at a high investment cost. This results in a substantial reduction in energy cost comparable to the incremental investment cost. From this, we see that most of the up-front investment in the transport sector can be paid back by annual energy cost savings over the lifetime of the technology.
In this article we examine the technological feasibility of the global target of reducing GHG emissions to 50 % of the 1990 level by the year 2050, a level roughly aligned with the climate target of 2 °C. We also assess the transition of energy systems in major energy sectors such as power generation, industry, transport, and buildings. Lastly, we perform a detailed analysis of the contribution of low-carbon technologies to GHG emission reduction and evaluate the required technological cost. An important component of this study, a detailed assessment of technologies in energy and non-energy sectors in mid- and long-term timeframes, sets it apart from other studies on the same topic.
The analysis leads to the following conclusions:
The target of reducing GHG emissions by 50 % from the 1990 level by the year 2050 is technically feasible, but will require great emission mitigation effort. The GHG emission reduction rates from the reference scenario stand at 23 % in 2020 and 73 % in 2050. The marginal abatement cost to achieve these emission reductions reaches $150/tCO2-eq in 2020 and $600/tCO2-eq in 2050.
The emission reduction target can be achieved by reducing energy intensity (energy consumption/GDP) by 55 % and reducing carbon intensity (CO2 emission/energy consumption) by 75 % by 2050.
Major changes in energy systems are required. For example, low/zero/negative-carbon technologies such as fossil fuel with CCS, wind, solar, and biomass with/without CCS become dominant in the power generation sector by 2050.
Energy saving and fuel switching, in combination with improvements in the emission factor of electricity, are key to achieving significant reductions in CO2 emissions in the final energy consumption sectors.
Renewable energy, fuel switching, and efficiency improvement in thermal power generation account for 45 % of the total GHG emission reduction in 2020. Non-energy sectors, namely, fugitive emission, waste management, agriculture, and F-gases, account for 25 % of the total GHG emission reduction in the same year.
CCS, solar power generation, wind power generation, biomass power generation, and biofuel collectively account for 64 % of the total GHG emission reduction in 2050.
The required additional investment in GHG abatement technologies reaches US$ 6.0 trillion by 2020 and US$ 73 trillion by 2050. These investments correspond to 0.7 and 1.8 % of the world GDP, respectively, in these periods.
Non-Annex I regions account for 55 % of the total additional investment by 2050.
Among all sectors, the largest investment is required in power generation. The power generation sector accounts for 56 % of the total additional investment by 2050.
The transport sector accounts for 30 % of the total additional investment by 2050. Most of the investment in the transport sector, however, can be paid back through energy cost savings.
In this article, ‘mid-term’ refers to the period up to 2030 and ‘long-term’ refers to the period beyond 2030, unless otherwise noted.
An important step, for long-term energy planning, is to evaluate the energy system from a risk management perspective. Currently, in the aftermath of the nuclear power reactor accident in Fukushima, the assessment of environmental and social risks associated with technological and natural uncertainties is thought to be particularly important. Yet this type of assessment lies outside the scope of this study. Instead, we focus on the costs and mitigation potentials of low-carbon technologies.
Bioenergy supply is assumed to cause no major land use change or additional CO2 emission in any of the scenarios in this study. See “Key assumptions on the availability of resources and technologies” for more detail.
This is a rough approximation of the relationship between bioenergy supply and CO2 emission from land use change. More detailed analysis on bioenergy utilization and CO2 emission requires an integrated modeling approach on energy and land use. Yet this type of analysis remains to be done.
The nuclear power plant accident in Fukushima may increase scepticism about the safety of nuclear power plants and persuade some countries to scale down their nuclear policies. Some countries, in fact, have already announced plans to phase out their nuclear plants. Overall, however, the impact of the Fukushima nuclear accident over long-term nuclear policies around the world remains to be seen. Therefore, this impact is not considered in this study.
AIM/Enduse[Global] includes integrated biomass gasification combined cycle (biomass IGCC) with CCS as an option for power generation. Biomass IGCC is a promising biomass power generation technology considered both highly efficient and economically feasible, as it is technically similar to the efficient coal IGCC process and can profit from the experiences gained with coal IGCC plants (Rhodes 2007). When biomass IGCC and CCS are integrated in a combined system, nearly all CO2 can be captured (Luckow et al. 2010). Yet biomass IGCC is still in the demonstration phases: only a few demonstration plants have been built so far.
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This research was supported by the Environment Research and Technology Development Fund (S-6-1 and A-1103) of the Ministry of the Environment of Japan.
This article is distributed under the terms of the Creative Commons Attribution License which permits any use, distribution, and reproduction in any medium, provided the original author(s) and the source are credited.
Handled by Tatsuya Hanaoka, National Institute for Environmental Studies, Japan.
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Akashi, O., Hanaoka, T. Technological feasibility and costs of achieving a 50 % reduction of global GHG emissions by 2050: mid- and long-term perspectives. Sustain Sci 7, 139–156 (2012). https://doi.org/10.1007/s11625-012-0166-4