Since the industrial revolution, U.S. greenhouse gas (GHG) emissions have risen steadily in most years, in tandem with an economy fueled by fossil fuels. In recent years, however, the correlation between U.S. economic growth and emissions has weakened. After peaking in 2007, emissions have declined in 7 of the past 11 years, falling 11 percent from 2007 to 2018 (EPA, 2020) even as the economy grew by 19 percent over the same time (OMB, 2020). Nonetheless, emissions are not declining in all economic sectors, and the transition to a zero-carbon economy is not occurring fast enough to meet climate targets.
As discussed in Chapter 1, the United States emits about 6.7 billion metric tons of carbon dioxide equivalent (Gt CO2e) each year, of which roughly 80 percent is carbon dioxide (CO2), with the remainder split between methane (10 percent), nitrous oxide (7 percent), and the fluorinated gases (F-gases) (3 percent). Positive changes in land use and forestry offset about 700 million metric tons of carbon dioxide annually, with the result that net U.S. GHG emissions have hovered around 6 billion metric tons of CO2e over the past several years (2018 data, from EPA, 2020).
As shown in Figure 2.1, when all GHG emissions, including from electricity generation, are distributed by end-use sector, buildings account for the largest share of gross emissions at 32 percent, followed by industry (29 percent), transportation (28 percent), and agriculture (10 percent). When electricity emissions are considered separately, transportation is the top source of direct emissions (28 percent), followed by the electric power sector (27 percent), industry (22 percent), commercial and residential buildings (12 percent), and agriculture (10 percent) (EPA, 2020).
Electric power generation has been the real workhorse of emissions reductions, with carbon dioxide emissions from electricity generation declining by a third from 2005 to 2019 (EIA, 2020a). This decrease resulted from the replacement of the oldest, least-efficient coal plants with output at plants that burn natural gas (up 15 percentage
points of U.S. market share from 2009), and renewable energy, primarily variable generation from wind (up 5.5 percentage points) and solar (up 2 percentage points) (EIA, 2020b). Rapid declines in power sector emissions have been facilitated by the low cost of extracting natural gas from shale formations and precipitous declines in the cost of new solar photovoltaics (PVs; 89 percent cheaper since 2009) and new wind facilities (70 percent cheaper since 2009) (Lazard, 2019). All three of these trends have been driven by proactive public policy support, although these technologies were nascent and still costly (Trembath et al., 2012; Cox et al., 2015; Nemet, 2019; DOE-EERE, 2020b).
Thanks to ongoing policy support and steady innovation by the private sector (and preferences among many corporations for renewable power), the electricity sector could deliver as much as 90 percent clean electricity by 2035 at rates comparable to today’s levels. Such an outcome could occur by retaining existing hydropower and nuclear capacity, accelerating deployment of wind and solar to displace coal and some gas-fired generation, retaining most existing natural gas power plants for reliability and flexibility purposes, and building out sufficient electric transmission capacity to connect new renewable generation to the grid (Phadke et al., 2020).
However, there are limits to the quantity of cost-effective emissions reductions achievable with mature technologies, even in the power sector. Even taking into consideration the future coal-plant retirements that have already been announced, there could still be significant coal plant capacity online by 2030, unless competitive pressure increases over time (EIA, 2020c). Some of the remaining coal plants are owned by traditional investor-owned and publicly owned utilities, with their coal-plant investment costs included in the utility’s rate base and recovered through retail rates, and are
therefore partially shielded from market forces. Additionally, some coal plants provide local reliability service and may not be able to retire unless their capacity is replaced in the near term with sufficient amounts of other resources (e.g., new gas-fired capacity) capable of providing such services, and it may be difficult, if not impossible, to get approvals for such new fossil units. Also, some existing nuclear reactors have been unable to recover their costs in competitive wholesale markets, in part because current markets do not value the carbon-free attribute of electricity generated from nuclear plants. This is especially true for single-unit nuclear power plants and those that are not supported by state policies (e.g., New Jersey’s Zero Emissions Certificate Law). The retirement of nuclear power plants will need to be offset by additional net-zero carbon generation to continue making forward progress toward decarbonization goals. While natural gas plants can continue to provide reliability and flexibility services in the near term, reaching a 100 percent carbon-free electricity sector will ultimately require deployment of one or more “clean firm” electricity sources, including geothermal energy, biogas, nuclear energy, natural gas with carbon capture and sequestration (CCS), and hydrogen or other carbon-free fuels produced from net-zero carbon processes. Clean firm resources offer the benefit of carbon-free, dispatchable electricity that is available on demand for as long as needed without dependence on weather, and are thus critical complements to weather-dependent variable renewables and energy-constrained electricity storage technologies (Sepulveda et al., 2018).
Emissions from end-use sectors have not declined as rapidly, and in some cases have even increased. Since 2005, direct emissions (i.e., not accounting for electricity consumption) from transportation and industry declined by 5 percent and 2 percent, respectively. Emissions from agriculture and buildings grew by 5 percent and 6 percent (EPA, 2020). Across the end-use sectors, the story has been remarkably consistent: Increased activity in each sector has been partially offset by moderate levels of efficiency improvements, resulting in only incremental changes in emissions. In the transportation sector, growth in vehicle miles traveled has been offset by improved fuel economy. In the industrial sector, increased economic output has been offset by a combination of more efficient industrial processes and structural changes in the economy (e.g., a shift away from energy-intensive manufacturing to the services industry). And in the buildings sector, growth in floor space has been offset by improved efficiencies of buildings and appliances.
Deep decarbonization of the transportation, industry, and buildings sectors will require taking full advantage of a broader suite of decarbonization tools, including (1) accelerating improvement in end-use efficiency to reduce total fuel and materials demand; (2) substituting hydrocarbon fuels with carbon-free electricity; (3) using “drop-in” hydrocarbon fuels with net-zero lifecycle GHG emissions; and
(4) using CCS, enhanced land carbon sinks, or increases in negative emissions technologies (NETs) to capture or offset emissions from residual fossil fuel use.
This interim report focuses on actions to decarbonize the U.S. economy as part of efforts to reduce net GHG emissions—across all gases—to zero by midcentury. Figure 2.2 provides an illustrative path to achieving net-zero emissions, in which gross carbon dioxide emissions from the end-use sectors are almost completely eliminated, and negative emissions technologies are scaled up to offset residual emissions from hard-to-abate energy sectors. Non-CO2 gases and land sinks are discussed in Box 2.1.
Some end-use subsectors will be difficult (or prohibitively expensive) to decarbonize completely by 2050. In particular, aviation and shipping are more challenging to electrify than other transportation sectors, and low-carbon fuels may not reach sufficient scale by midcentury. Many industrial sectors, such as cement, iron, and steel and chemicals manufacturing, pose unique decarbonization challenges—for example, decarbonization options for high-temperature heat (Friedmann et al., 2019) and industrial process emissions (de Pee et al., 2018; Rissman et al., 2020), and sector-specific integration challenges. While technologies exist to cut emissions in these sectors,
they remain at precommercial or first-of-a-kind demonstration stages and require significant improvement in cost and performance to become commercially viable. Proactive innovation and maturation of emerging technologies over the next decade could ultimately supply a range of decarbonization options, even in these difficult-to-decarbonize sectors, but the feasibility of complete decarbonization by 2050 remains uncertain. Negative emissions technologies such as direct air capture and storage (DACS) and bioenergy with carbon capture and sequestration (BECCS) may be needed to offset these residual emissions, and provide additional tools in the decarbonization toolkit. To achieve net-zero CO2 emissions, residual emissions from the energy end-use sectors and negative emissions must sum to zero.
This report builds on a rich literature of research exploring what a net-zero emissions economy looks like and how to make this transition. Previous deep decarbonization studies vary in their specific technology and policy recommendations, but all share several common core elements. Specifically, the studies promote pathways that combine the following:
Most importantly, these analyses find that deep decarbonization is technically feasible at relatively low cost.
Deep decarbonization studies find that reaching net-zero emissions is technically feasible (and relatively low cost) provided that significant proactive effort is invested over the next decade to drive the maturation and improvement of a range of more nascent
technologies and solutions needed to reach net-zero emissions. For example, the International Energy Agency (IEA) finds that nearly half of the global annual emissions reductions necessary to achieve a net-zero energy system by 2050 will likely have to come from technologies that are currently at the demonstration or prototype stage of development but are not yet commercially available (IEA, 2020a). Although nascent, all of these technologies are technically feasible and do not require fundamental scientific “breakthroughs” in order to be deployed (although continued and expanded investment in scientific research can contribute further solutions not yet considered above). The challenge today is to drive the scale-up, maturation, cost reduction, and steady improvement of the full suite of low-carbon solutions. The history of successful energy innovations points the way forward.
Over the past decades, the United States has seen precipitous declines in the cost of five key technologies: wind power, solar power, shale gas, light emitting diodes (LEDs), and lithium-ion batteries for electric vehicles and grid-connected electricity storage (Trembath, 2012; DOE, 2015a). Deployment of these technologies has helped to bring about the bulk of emissions reductions to date and has transformed the economics of decarbonization. In each case, these remarkable trends were influenced by similar processes involving both proactive public investment in research, development, and demonstration (RD&D) and the creation of markets to hasten early adoption and ignite private sector innovation and competition through incentives and standards. Examples include the unconventional gas tax credit for shale gas, production and investment tax credits for wind and solar, utility rebate programs for LEDs, and fuel economy and zero emissions vehicle standards and electric vehicle subsidies for lithium-ion batteries. Thanks to prior decades of investment and policy, all five of these technologies went from expensive “alternative energy” to cost-competitive, mainstream energy choices that are transforming the electricity, buildings and appliances, and transportation sectors and will enable cost-effective and sustained reductions in GHG emissions over decades to come. Now, even as the United States targets deployment of these technologies at scale, the task remains to use this same successful engine of innovation to complete the net-zero carbon toolkit.
Under a business-as-usual scenario, U.S. energy consumers across residential, commercial, industrial, and other sectors are likely to spend more than $1 trillion annually on energy services between now and 2050 (EIA, 2019). This level of spending, including investment dollars that underpin it, provides an opportunity to leverage and redirect investment and expenditures toward a clean energy system.
Historical expenditures on energy ranged from 5.5 percent to nearly 14 percent of gross domestic product (GDP) for much of the period from 1970 through 2018 (EIA, 2020d).
Global and domestic spikes in the price of natural gas and oil have historically driven energy expenditures to the higher end of the range (as high as 9.6 percent of GDP as recently as 2008 [EIA, 2020d]). These spikes have exposed U.S. consumers and the economy to risks that could be substantially insulated if the nation were to build a net-zero emissions economy.
Multiple studies estimate that net-zero emissions could be achieved while spending roughly 4–6 percent of GDP on energy in total (Haley et al., 2019; Larson et al., 2020). Energy system expenditures in a net-zero emissions economy are likely to be higher than a business-as-usual pathway—Princeton’s Net-Zero America study (Larson et al., 2020)
estimates cumulative incremental cost (net present value, NPV) of $4 trillion to $6 trillion from 2020 to 2050 relative to a reference case. However, adopting a net-zero economy in the United States would reduce the risks of spikes in fossil markets and reduce the share of economic activity spent on energy services relative to today’s levels, while also eliminating the U.S.’ ongoing contributions to climate change. Estimates of the incremental cost of a net-zero transition have been decreasing over time as the costs of clean energy technologies (e.g., wind, solar, and electric vehicles) have been declining, indicating that innovation can further decrease the costs of the clean transition.
Any pathway to decarbonization entails fundamental shifts in the way Americans power their homes and economies, produce goods, deliver services, transport people and goods, and manage public and private lands. This transition is bounded by societal expectations of reliability and costs of energy services and products, considerations of energy access and equity, uncertainties in the pace of technology development and deployment, and regulatory and market barriers to new technologies (EFI, 2019). The energy system has considerable inertia, aversion to risk, and market, finance, and regulatory structures that favor incumbents. Previous experiences have demonstrated that widespread adoption of new technologies is facilitated by perceived value, clear communication, and consumer incentives. For example, much of the success of the ENERGY STAR program can be attributed to its recognizable and easily understandable labeling and purchase incentives, in addition to consumer desire for improved energy efficiency (EPA, 2017). Similarly, Tesla offers vehicles that have both desirable performance features as well as decarbonization benefits. Societal preferences and policy, regulatory, and investment environments will constrain and shape the transition (EFI, 2019). These ideas are further discussed in Chapter 3.
Slow stock turnover in buildings, industrial facilities, and other long-lived assets leaves little room for delay and few opportunities to replace or repurpose existing infrastructure for a low-carbon energy system (Figure 2.4). Deep decarbonization can be achieved without retiring existing equipment and infrastructure before the end of their economic lifetime, which reduces the cost of the transition (Williams et al., 2014). However, long-lived infrastructure, such as power plants, buildings, and many industrial facilities and equipment, has only one natural replacement cycle before midcentury. As these assets are replaced, the new equipment must be consistent with
the net-zero transition path in order to achieve net zero at the lowest total cost. Failure to replace retiring infrastructure with efficient, low-carbon successors will either result in the inability to meet emission-reduction targets or require early retirement of the replacement equipment, leading to sunk costs and stranded assets.
Recent studies see the 2020s as the time to build out enabling infrastructure for the net-zero transition and end most new investments in infrastructure to transport fossil fuels (e.g., pipelines) (Williams et al., 2018; Farbes et al., 2020; Kwok et al., 2020). Required infrastructure developments include electric vehicle (EV)-charging
infrastructure for vehicles and long-distance high-voltage transmission lines (Podesta et al., 2019; Haley et al., 2019; Phadke et al., 2020), as well as hydrogen transport and storage infrastructure and with the need to plan for CO2 infrastructure, including pipelines and storage, to come online during the 2030–2035 period (Larson et al., 2020). Efforts to site and permit new infrastructure projects must be initiated soon, given the challenges associated with obtaining permits and the long build-times. For example, new transmission lines, which are needed to connect renewable resources to areas of high electricity demand, can take as long as 16 years, and an average of 8–10 years, to site and permit (Reed et al., 2020).
Repurposing existing energy infrastructure could play a key role in enabling a clean energy future by reducing the overall costs of the transition to clean energy, as well as mitigating likely opposition to the needed transition by reducing the potential for stranded investments and workers (EFI, 2019). For example, upgrading or converting natural gas pipelines to carry hydrogen/natural gas blends or 100 percent hydrogen could help retain the use of those pipelines in a low-carbon energy system, avoiding the need for more costly and difficult-to-site new builds while also preventing stranded assets for pipeline owners and preserving jobs in natural gas transmission and distribution utilities. Using residual oil and gas basins for permanent underground storage of carbon dioxide could help oil companies transition into carbon management utilities. Maximizing the use of existing infrastructure would help create greater buy-in for companies and their employees who benefit from the current carbon-intensive economy.
Reaching net-zero emissions is much more challenging and requires a different set of low-carbon resources than a system with more modest reductions. For example, modest emissions reductions in the power sector (e.g., 50–70 percent CO2 reductions) can be achieved with deployment of natural gas-fired power plants. However, transitioning to near-zero emissions from electricity generation requires replacing the vast majority of fossil fuel power plants or equipping them with carbon capture technologies (Jenkins et al., 2018). Similarly, moderate transportation sector reductions can be achieved by blending conventional biofuels with petroleum-based transportation fuels. However, there is strong agreement in the literature that decarbonizing transportation entails the phase-out of internal combustion engine (ICE) vehicles and
replacement with electric drivetrains, including battery electric and fuel cell vehicles. Policies that produce incremental reductions in emissions without facilitating transformation can lead to technology lock-in and emissions cul-de-sacs that make deep decarbonization by midcentury unattainable (Williams et al., 2014).
Decarbonization pathways differ in their varied mixes of policies and the central technologies upon which they depend. Some pathways are constructed using least-cost models that deploy or retire energy infrastructure based on the lowest cost of meeting energy demand without emissions. Least-cost models generally employ a broad range of zero-carbon technologies, although such models may not account for permitting and siting, regulatory, financing, or other barriers. Sometimes, lowest-cost pathways from a techno-economic or engineering perspective overlook costly impacts on certain communities or minimize or ignore friction in markets that make it difficult to accomplish those least-cost approaches.
Some other pathways are constructed using a preferred set of technologies, such as 100 percent renewables scenarios (in the electricity sector or economy wide). Still others are developed by envisioning different policy pathways, such as pathways that rely heavily on technology-neutral carbon prices or clean energy standards.
In general, decarbonization modeling finds that scenarios that constrain available technology options result in higher overall mitigation costs than scenarios that are technology neutral. For example, the Intergovernmental Panel on Climate Change (IPCC) Fifth Assessment Report determined that mitigation costs increased by 138 percent in models with no CCS (IPCC, 2014), and Sepulveda et al. (2018) found that decarbonizing the electricity sector is 11 to 163 percent more expensive if all clean-firm power generation technologies such as nuclear, CCS, and bioenergy are excluded.
More difficult to quantify, but just as important, scenarios that remove viable options generally present a greater risk of failure, as they depend more heavily on scale-up of favored technologies without impediment by any social, financial, regulatory, or other barriers. An effective risk-management strategy would hedge against likely failure modes by investing in low-carbon technologies or strategies that may prove unnecessary in a favored scenario, but provide critical alternatives should one or more bottlenecks slow progress.
All plausible pathways to zero emissions share core features: decarbonizing electricity; switching to electricity and other low-carbon fuels for energy services in the transportation, industry, and buildings sectors; increasing energy efficiency in each of those sectors, in the power sector, and in materials; increasing carbon sequestration, and reducing emissions of non-carbon climate pollutants.
In particular, there is strong agreement among deep decarbonization studies on the following points:
Feasible decarbonization pathways are very similar in the first 10 years and diverge only in later years. This first report focuses on near-term priority decarbonization actions for 2021–2030 that are robust across many scenarios or retain optionality in the face of uncertainty about the final decarbonization pathway. The committee’s assessment of decarbonization approaches and pathways from 2021–2050 will be discussed in its second report.
Analyses that model pathways to net-zero emissions in 2050 agree that in the next 10 years, the United States must:
This report builds on the existing, robust literature on possible pathways to deep decarbonization. Metrics for three of the most recent and comprehensive studies are reported in more detail in Table 2.1. The scenarios analyzed in these studies projected energy demand, share of non-emitting electricity, share of electricity in final energy demand, energy productivity, and scale of CCS, land sinks, hydrogen production, impact of non-CO2 gases, building energy intensity, and EV share. Table 2.1 compares both their 2030 and 2050 results. Although these studies and models rely on different assumptions, data, and methods, the comparison in Table 2.1 illustrates their coherence in the first 10 years in particular.
No model currently exists in the public domain that is capable of modeling all major elements of a net-zero system at the requisite level of detail to analyze: deep reductions in energy demand through efficiency in vehicles, appliances, buildings; flexible central-station and distributed resources (including flexible demand) at dispatch time scales; power flows and realistic expansion of local and high-voltage electricity networks; gas and liquid fuels production, transportation, storage, and consumption; CO2 capture, pipelines, use, and sequestration; and non-CO2 greenhouse gases and carbon sinks. The primary technical impediment to developing such a model is computational constraints, because the model must simultaneously optimize decisions across all sectors, at high temporal resolution (to capture flexibility needs and
TABLE 2.1 Relevant Metrics/Indicators Across Three Separate Decarbonization Studies
| Key Metric | 2015a | 2030 | 2050 | ||||
|---|---|---|---|---|---|---|---|
| Energy Innovationb | Deep Decarbonization Pathways Projectc | Net-Zero America Projectd | Energy Innovation | Deep Decarbonization Pathways Project | Net-Zero America Project | ||
| Final Annual Energy Demand (quads) | 97 | 129 | 80 | 64–67 | 125 | 65 | 50–56 |
| Percent Non-emitting electricity | 18 | 60 | 55 | 62–77 | 100 | 85 | 98–100 |
| Electricity share of final energy demand (percent) | 28 | 44 | 32 | 21–25 | 73 | 60 | 38–51 |
| Energy productivity of GDP ($ economic output per energy) ($ billion/quad)e | 185.5 | 182 | 293 | 350–367 | 272 | 524 | 609–682 |
| Carbon capture (MMT CO2/yr) | 0 | 30.6 | ND | 65–197 | 26 | 775 | 690–1760 |
| Land sinks (MMT CO2/yr) | 760 | 245 | 1050 | 750 | 630 | 1050 | 850 |
| Hydrogen production (quads/yr) | 0.74f | 2.5 | <1 | 0.95–1.9 | 5.5 | <1 | 7–18 |
| Non-CO2 gases (MMT CO2e/yr) | 1264 | 1243 | ND | 1090 | 587 | ND | 1020 |
| Key Metric | 2015a | 2030 | 2050 | ||||
|---|---|---|---|---|---|---|---|
| Energy Innovationb | Deep Decarbonization Pathways Projectc | Net-Zero America Projectd | Energy Innovation | Deep Decarbonization Pathways Project | Net-Zero America Project | ||
| Building energy demand (quads/yr) | 18 | 17 | 16.4 | 18–19 | 11 | 13 | 13–15 |
| EV share of light-duty vehicle stock (percent) | 1 | 47 | 44 | 6–17 | 100 | 100 | 61–96 |
a EIA 2019a, 2020a; EPA, 2019, 2020; White House, 2016.
c Haley et al., 2019. Follows EIA projections for economic growth and increased consumption of “energy services.” Assumes rapid adoption of electrification technologies and high-efficiency technologies where the end-use is already electric (i.e., refrigeration) or where complete electrification is infeasible. Adoption rates of these technologies accelerate through 2030, with the stock of these technologies lagging but making steady progress through 2050. Assumes an enhanced land sink 50 percent larger than the current annual sink. Assumes that nuclear plants already in operation will be operated and retired based on the schedule in the 2017 Annual Energy Outlook.
e Calculated using data from PWC, 2017.
f D. Brown, 2016. U.S. Hydrogen Production—2015. CryoGas International.
NOTE: These studies, while conducted with different modeling frameworks and assumptions, find commonality in the near term and greater divergence in the long term. This comparison illustrates agreement in the literature regarding near-term actions to begin a long-term energy transition and underscores the importance of actions that maintain or enhance optionality in the long term. ND = not determined.
impacts of variable renewable electricity production), and with sufficient geospatial detail to capture complex variations in demand, siting limitations, and local policies and to provide actionable insights to inform real-world decision making. New tools and ways of thinking about energy system models will be required to overcome these barriers. The United States should invest in the development of an ecosystem of open-access modeling tools and open-source data to accurately parameterize these models to help plan the transition to net zero and to better represent the universe of possible net-zero transitions.
This report identifies 10-year actions that are robust across decarbonization pathways. The committee emphasizes strategies that are (1) “no-regrets” actions that would be needed regardless of the final path taken or (2) that retain “optionality” and flexibility so that the United States can take advantage of technological advances, mitigate risks that could derail primary strategies, and avoid stranded actions. Such an approach is also important in light of uncertainties in technology, support for climate policy, differences in regional energy resources or stakeholder preferences, and future climate impacts. The final report focusing on a longer time period will need to consider more strongly methods for planning and policy making under deep uncertainty (Marchau et al., 2019; Mathy et al., 2016; Waisman et al., 2019; Bataille et al., 2016). However, identifying a strategy for 2021–2030 is easier than it sounds, because feasible paths for near-term emissions reductions and early investment in long-term potential strategies are very similar in the first 10 years and diverge only in later years.
For these strategies, the committee has provided estimates of the pace and depth of needed technology deployment and action, in order to provide the order of magnitude of changes warranted in a no-regrets strategy and set of actions in the next 10 years. A selection of these is summarized in Table 2.3 below.
Energy and materials efficiency is one of the most cost-effective near-term approaches to reduce energy demand and associated emissions. This approach includes adopting developing technologies and processes that increase fuel efficiency of vehicles (on-road and off-road, including farming equipment); increasing the efficiency of building enclosures as well as installing efficient appliances and equipment in buildings; enhancing energy productivity in manufacturing and other industrial processes and in the power generation fleet; and improving systems efficiencies from greater energy system integration. Demand efficiency and materials efficiency measures (e.g., recycling and reuse)
are also included in this category. Priority actions in the 2021–2030 time frame include the following:
Electrification of energy services, in tandem with decarbonization of electricity generation, has emerged as a core element in nearly all deep decarbonization scenarios. The greatest near-term (2021–2030) potential for electrification is in the buildings and transportation sectors. In buildings, electric heat pumps for space conditioning and water heating can help lower carbon emissions compared to fossil systems. Among LDVs, electric vehicles are projected to reach cost-parity with internal combustion engine vehicles in the next decade and, in conjunction with relatively low-carbon electricity, will also reduce emissions. Some potential exists for electrification of industrial processes, although electrification technologies for the industrial sector are at a relatively early stage of development and play a greater role beyond the 2030 time frame, as electrification technologies mature, decline in cost, and are demonstrated at scale.
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1 Climate zones are based on heating degree days, average temperatures, and precipitation. Climate zones 1–5 cover all of the United States except for the “cold,”“very cold,” and “subarctic” regions that include Alaska, the northern half of Rockies, the Upper Plains states, Minnesota and Wisconsin, northern Michigan, upstate New York, and the northern half of New England (DOE, 2015b).
The electric sector plays a critical role in decarbonization, both in terms of reducing GHG emissions from electricity production and use and for supporting the decarbonization of other sectors. Since 2005, the share of electricity from zero-carbon emitting sources—including nuclear power, hydropower, wind, solar, biomass, and geothermal—has increased from 28 percent to 37 percent. This growth comes primarily from wind and solar, as cost reductions and policy incentives have combined to drive deployment (even as other zero-carbon emitting technologies have declined or remained stagnant). Wind or solar power is now the cheapest source of new electricity generation in 34 percent of U.S. counties, based on levelized cost of electricity and considering regional differences in capital costs and fuel delivery prices (UT-Austin, 2020).
The 2020s are a key decade to build out the electric transmission and distribution infrastructure needed to accommodate flows from and access to these commercially ready new zero-carbon resources.
In the 2020s, efforts must begin to build out enabling infrastructure for the low-carbon transition. These will include EV-charging networks (to enable vehicle
electrification); long-distance high-voltage transmission lines (to bring remote power resources to population centers, because high-quality renewable sources are often not located near major load centers); upgrades to distribution grid upgrades to enable electrification of heating and transport; and renewable fuel (e.g., hydrogen) transport and storage infrastructure. Planning and siting for a national CO2 pipeline system should begin immediately, and various developments in the first half of the decade will determine whether CO2 infrastructure, including pipelines and storage, will need to be built at scale by 2030 or the middle of the next decade.
For some sources of emissions, and particularly those in harder-to-abate sectors, low-carbon alternatives are still in the pilot stage or remain nascent industries. For these sectors, near-term opportunities for emissions reduction are limited to improving energy efficiency, materials efficiency, demand management, and other tools that reduce—but cannot completely eliminate—the emissions intensity of these sectors. Maturation, improvement, and scale-up of an expanded set of carbon-free alternatives will be needed as near-term emission reduction opportunities are exhausted. Bringing new energy technologies to market can take 20–70 years from the first prototype, and driving maturation and cost declines for nascent industries proceeds over a decade or longer time scales. Therefore, proactive RD&D and market creation efforts are needed in the 2020s to develop, improve, and scale up nascent low-carbon energy technologies, including the following:
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2 Ultramafic rock is igneous in nature.
Many recent studies estimate that from a technical point of view, the United States could transition to net zero by 2050 using only commercial and near-commercial technologies and spending a smaller fraction of the nation’s GDP on energy system expenditures3 than the country has in the past, including the past decade (see Figure 2.3). However, energy system expenditures during a net-zero transition would be significantly greater than business as usual. If technological options improve faster than considered in recent modeling studies, then the cost of decarbonization could prove lower.
Studies reviewed by the committee in this chapter (Larson et al., 2020; SDSN, 2020) indicate that cumulative incremental energy system expenditures during a net-zero energy transition would be approximately $100 billion to $300 billion through 2030, and $4 trillion to $6 trillion through 2050 beyond the $22.4 trillion in a business-as-usual baseline. (These estimates are reported on a NPV basis of cumulative total expenditures with a 2 percent real social discount rate.4 With a 5 percent social discount rate, the impact would be $210 billion to $270 billion through 2030 and $2 trillion to $3 trillion through 2050. These estimates do not provide a commensurate indicator of the benefits of these investments.) It is important to note that these estimates of energy costs do not capture general equilibrium effects, such as changes in global oil prices. Note, however, that a net-zero transition would greatly reduce U.S. oil demand and put substantial downward pressure on prices. Nor do these cost estimates include impacts of changes in the U.S. balance-of-trade and other effects, which include both positive and negative factors.
The costs for deep decarbonization also must be considered in the context of the considerable benefits of a clean energy transition that could offset some, all, or more than the cost of the transition. There are climate benefits, new economic and employment opportunities, substantial improvements in public health, and intangible global leadership credentials. For example, Hsiang et al. (2017) estimate U.S. economic losses of 1.2 percent of GDP per 1°C temperature rise, with risk distributed unequally across the country and the poorest third of counties in the United State projected to incur the largest damages. They estimate the mitigation of economic damages of $200 billion to $300 billion annually by 2100 compared to a business-as-usual course.
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3 The energy system expenditures referenced here encompass both energy supply and demand, but do not include capital investments.
4 Discount rates put a present value on future costs and benefits. Social discount rates attempt to value the cost and benefits for future generations relative to costs and benefits today.
Benefits of a net-zero transition also include reductions in premature deaths owing to reduced air pollution from fossil fuels, with the magnitude ranging by study: a reduction of 85,000 total premature deaths from air pollution over the 2020–2050 time period from decarbonizing electricity (Phadke et al., 2020); a reduction of 11,000 to 52,000 annual premature deaths from the elimination of air pollution from coal power plants (Prehoda and Pearce, 2017; Larson et al., 2020); and a reduction of up to 200,000 annual premature deaths from eliminating air pollution from fossil fuels entirely (Lelieveld and Münzel, 2019). In addition, a recent report estimated 5 million sustained jobs could be associated with electrifying most energy uses beyond an even larger initial surge of the infrastructure deployment (Griffith and Calisch, 2020), although this would be offset by the loss of about 1.6 million jobs in fossil fuel related sectors. Another recent study estimates that a net increase of roughly 1 million to 5 million jobs would be supported by energy supply-related sectors by 2050 (0.5–1 million by 2030), as total employment in wind, solar, transmission, and other growing sectors offset losses in oil, gas, and coal, in aggregate (Larson et al., 2020). The committee’s task directed it to focus on mitigating emissions, and therefore these beneficial impacts are not extensively reviewed. However, it is clear there are substantial benefits of a net-zero transition.
Figure 2.5 and Table 2.2 summarize the roughly $2 trillion in incremental capital investments that must be mobilized over the next decade for projects that come online by 2030 (i.e., total capital in service in the 2020s) to put the United States on track to net zero by 2050. This includes roughly $0.9 trillion in incremental capital investment in supply-side sectors and networks (roughly double the total capital expenditures under business-as-usual) and $1.2 trillion in incremental demand-side investments in buildings, vehicles, and industrial efficiency. It is important to note that these capital investments are not a direct cost borne by either taxpayers or energy consumers. They are investments in the U.S. economy made by both private and public sector actors. The sum of capital investments that must be mobilized in the 2020s is much larger than the increase in total consumer energy expenditures described above because capital investments are paid back through energy expenditures over many years and because investments in renewable electricity, efficient buildings and vehicles, and other capital-intensive measures offset significant annual expenditures on consumption of fuels.
Box 2.2 discusses potential synergies within the systems involved in a net-zero transition, including possible trade-offs and unintended consequences.
TABLE 2.2 Comparison of Supply-Side Capital Investment Needed Between 2021 and 2030 in Princeton Net-Zero America Study of High Electrification (E+) Net-Zero Pathway and Reference Scenario
| Supply Side—Total Capital Investment | Billion USD, 2021–2030 | ||
|---|---|---|---|
| Reference | Net-Zero (E+) | ||
| Electricity | Wind | 110 | 414 |
| Solar | 62 | 374 | |
| Natural gas CT and CCGT | 101 | 112 | |
| Natural gas with CCS | 0 | 0 | |
| Li-ion battery storage | 3 | 3 | |
| Biomass with CCS | 0 | 2 | |
| Networks | Electricity transmission | 203 | 356 |
| Electricity distribution | 352 | 369 | |
| EV chargers | 1 | 7 | |
| CO2 storage | 0 | 11 | |
| CO2 transportation | 0 | 68 | |
| Fuels and industry | H2—gas reforming | 3 | 3 |
| H2—gas reforming with CCS | 0 | 7 | |
| H2—biomass gasification with CCS | 0 | 0 | |
| Electric boilers | 0 | 12 | |
| Gas boilers | 5 | 5 | |
| Cements with CCS | 0 | 9 | |
| DRI steel | 0 | 0 | |
| Total supply side capital expenditure, 2021–2030 | 840 | 1,752 | |
NOTE: The Princeton Net-Zero America analysis (Larson et al., 2020) quotes both total capital in service for projects that come online from 2021 to 2030 and total capital mobilized, which includes capital being spent in the 2020s for projects that come online post-2030. This table quotes total capital in service. NOTE: CCS = carbon capture and sequestration; DRI = direct reduced iron. SOURCE: Data from Larson et al. (2020).
TABLE 2.3 Key Actions Necessary by 2030 for the Five Key Decarbonization Approaches in a Selection of Sectors
| Improve Efficiency and Energy Productivity | Electrify Energy Services in the Buildings, Transportation, and Industrial Sectors | Decarbonize Electricity | Build Critical Infrastructure | Innovate to Complete the Low-Carbon Toolkit | |
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NOTE: CCS = carbon capture and sequestration; EV = electric vehicle; ICE = internal combustion engine; RD&D = research, development, and demonstration.
The following topical boxes (Boxes 2.3 through 2.9) highlight the committee’s evaluation of technologies and approaches required in 2021–2030 to remain on the trajectory for full decarbonization by 2050, organized by sector. Energy demand, supply, carrier, and storage approaches are discussed, including needs for buildings, transportation, industry, energy storage, fuels, electricity generation and transmission, and carbon capture and sequestration. For each topic, the following aspects are highlighted:
The overall goals for a decarbonization policy plan and the beneficial policies to implement the needed emissions reduction approaches are discussed in Chapters 3 and 4, respectively.
Six overarching goals and strategies to achieve building demand reduction and decrease carbon emissions from the building sector are described below:
opportunity as well, delivering roughly 300–1,000 MtCO2/yr of negative emissions by 2050 (Larson et al., 2020) that can offset direct emissions elsewhere in hard-to-decarbonize sectors.
Avoiding CO2 emissions through capture at the point source requires less energy than capture from dilute air. However, direct air capture is receiving increased attention as an approach to offset difficult-to-eliminate emissions from the transportation, industrial heating, and agriculture sectors, and for other options in carbon removal (Wilcox, 2020a,b).
TABLE 2.9.1 Scale, Energy, Cost, and Example Carbon Capture Projects Globally
| Capture Application | 2020-Scale (MtCO2/yr)a | Percent CO2b | Min Work (kJ/mol)c | Nth-kind Costd ($/tCO2) | Example Projects (Start Date; Scale) |
|---|---|---|---|---|---|
| Natural Gas | 700 | 3–5 | ~9–10 | ~55–60 | Elk Hills, Fluor (2020; Mt/yr) |
| Industry (process emissions only) | |||||
| Cement | 67 | 25–30 | ~4 | ~30 | Lafarge Holcim, Total, Svante (2019; kt/yr) |
| Refining | 40 | 15–20 | ~6 | ~40 | Norway, Statoil Mongstad (2012; 100s kt/yr) |
| Bioethanol | 37 | 99+ | ~0 | ~<20 | Decator, ADM (2017; Mt/yr) |
| Hydrogen | 26 | 45–70 | ~2-3 | ~25–30 | Port Arthur, Air Products (2013; Mt/yr) |
| Iron and Steel | 19 | 20–25 | ~5 | ~35–40 | Abu Dhabi CCS Project, UAE (2016; Mt/yr) |
| Air Capturee | |||||
| Solvents | ~1 | 0.04 | 21 | ~150–600 | Carbon Engineering (2023; 1 Mt/yr) |
| Solid Sorbents | <1 | 0.04 | 21 | ~150–600 | Climeworks—14 plants globally (kt/yr) |
a Pilorgé et al., 2020; Psarras et al., 2020.
b Bains et al., 2017; Pilorgé et al., 2020; Psarras et al., 2020.
d Based on nth-of-a-kind technology-agnostic modeling from Pilorgé et al., 2020.
e Cost range is broad and depends on technology and energy resource choices, in addition to scale of deployment.
The many feasible pathways for deep decarbonization by 2050 all have similar requirements in 2021–2030, which are summarized in this report’s five key actions for the 2020s:
In order to remain on a path to decarbonization by 2050, decision makers in transportation, buildings, industry, electricity generation/transmission/distribution, fuels, and other sectors must align their actions with the five key actions. Some actions for 2021–2030 are already under way with existing technology and need to be maintained or accelerated, such as the steady installation of new zero-carbon electricity generation and retirement of coal-fired generation. Some actions could be implemented immediately with existing technology but need to begin, such as replacement of building heating with electric equipment, widespread deployment of electric vehicles, and blending of hydrogen with natural gas in industrial infrastructure and equipment. Other actions, such as carbon capture, require improvement and maturation of existing technologies or new technology or approaches to be developed and tested at scale, and research, development, and deployment in these areas must be accelerated in the decade after the release of this report to provide options in 2030–2050.
The investment requirements in 2021–2030 to implement the five key actions would require spending no more of the nation’s GDP on energy services than the United States has over the past decade and would require a total incremental expenditure of about $300 billion above the business-as-usual case through 2030 (an ~3 percent increase relative to business-as-usual). The transition to a decarbonized system would have significant benefits in the United States, on the order of $200 billion to $300 billion annually of avoided climate damages, in addition to preventing hundreds of thousands of premature deaths and saving trillions of dollars of health costs from fossil fuel pollution.
Although the approaches to decarbonization are well known, and the technologies to get started are ready for implementation in 2021–2030, new policies and systems are required to reduce cost and encourage adoption of needed technologies and
approaches at a sufficient pace and scale. The technological goals for a net-zero energy system by 2050 detailed in this chapter are complementary to the socioeconomic goals discussed in Chapter 3 and integral to the policy options presented in Chapter 4.
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