The U.S. Fourth National Climate Assessment, released in 2018, concluded that “the impacts of global climate change are already being felt in the United States and are projected to intensify in the future—but the severity of future impacts will depend largely on actions taken to reduce greenhouse gas [GHG] emissions and to adapt to the changes that will occur.” Members of Congress and stakeholders articulate a wide range of perspectives over what to do, if anything, about GHG emissions, future climate change, and related impacts. If Congress were to consider establishing a program to reduce GHG emissions, one option would be to attach a price to GHG emissions with a carbon tax or GHG emissions fee. In the 115th Congress, Members introduced nine bills to establish a carbon tax or emissions fee program. However, many Members have expressed their opposition to such an approach. In particular, in the 115th Congress, the House passed a resolution “expressing the sense of Congress that a carbon tax would be detrimental to the United States economy.”
Multiple economic studies have estimated the emission reductions that particular carbon tax would achieve. For example, a 2018 study analyzed various impacts of four carbon tax rate scenarios: a $25/metric ton of CO2 and $50/metric ton of CO2 carbon tax, increasing annually by 1% and 5%. The study concluded that each of the scenarios would likely achieve the U.S. GHG emission reduction target pledged under the international Paris Agreement (at least in terms of CO2 emissions).
A carbon tax system would generate a new revenue stream, the magnitude of which would depend on the scope and rate of the tax, among other factors. In 2018, the Congressional Budget Office (CBO) estimated that a $25/metric ton carbon tax would yield approximately $100 billion in its first year. CBO projected that federal revenue would total $3.5 trillion in FY2019.
Policymakers would face challenging decisions regarding the distribution of the new carbon tax revenues. Congress could apply revenues to support a range of policy objectives but would encounter trade-offs among the objectives. The central trade-offs involve minimizing economy-wide costs, lessening the costs borne by specific groups—particularly low-income households and displaced workers in certain industries (e.g., coal mining)—and supporting other policy objectives.
A primary argument against a carbon tax regards it potential economy-wide impacts, often measured as impacts to the U.S. gross domestic product (GDP). Some may argue that projected impacts should be compared with the climate benefits achieved from the program as well as the estimated costs of taking no action. The potential impacts would depend on a number of factors, including the program’s magnitude and design and, most importantly, the use of carbon tax revenues.
In general, economic literature finds that some of the revenue applications would reduce the economy-wide costs from a carbon tax but may not eliminate them entirely. In addition, some studies cite particular economic modeling scenarios in which certain carbon tax revenue applications produce a net increase in GDP compared to a baseline scenario. These scenarios involve using carbon tax revenues to offset reductions in other tax rates (e.g., corporate income or payroll taxes). Although economic models generally indicate that these particular revenue applications would yield the greatest benefit to the economy overall, the models also find that lower-income households would likely face a disproportionate impact under such an approach. As lower-income households spend a greater proportion of their income on energy needs (electricity, gasoline), these households are expected to experience disproportionate impacts from a carbon tax if revenues were not recycled back to them in some fashion (e.g., lump-sum distribution).
A price on GHG emissions could create a competitive disadvantage for some industries, particularly “emission-intensive, trade-exposed industries.” Policymakers have several options to address this concern, including establishing a “border carbon adjustment” program, which would levy a fee on imports from countries without comparable GHG reduction programs. Alternatively, policymakers could allocate (indefinitely or for a period of time) some of the carbon tax revenues to selected industry sectors or businesses. Relatedly, a carbon tax system is projected to disproportionately impact fossil fuel industries, particularly coal, and the communities that rely on their employment. To alleviate these impacts, policymakers may consider using some of the revenue to provide transition assistance to employees or affected communities.
The U.S. Fourth National Climate Assessment, released in 2018, concluded that "the impacts of global climate change are already being felt in the United States and are projected to intensify in the future—but the severity of future impacts will depend largely on actions taken to reduce greenhouse gas [GHG] emissions and to adapt to the changes that will occur." Members of Congress and stakeholders articulate a wide range of perspectives over what to do, if anything, about GHG emissions, future climate change, and related impacts. If Congress were to consider establishing a program to reduce GHG emissions, one option would be to attach a price to GHG emissions with a carbon tax or GHG emissions fee. In the 115th Congress, Members introduced nine bills to establish a carbon tax or emissions fee program. However, many Members have expressed their opposition to such an approach. In particular, in the 115th Congress, the House passed a resolution "expressing the sense of Congress that a carbon tax would be detrimental to the United States economy."
Multiple economic studies have estimated the emission reductions that particular carbon tax would achieve. For example, a 2018 study analyzed various impacts of four carbon tax rate scenarios: a $25/metric ton of CO2 and $50/metric ton of CO2 carbon tax, increasing annually by 1% and 5%. The study concluded that each of the scenarios would likely achieve the U.S. GHG emission reduction target pledged under the international Paris Agreement (at least in terms of CO2 emissions).
A carbon tax system would generate a new revenue stream, the magnitude of which would depend on the scope and rate of the tax, among other factors. In 2018, the Congressional Budget Office (CBO) estimated that a $25/metric ton carbon tax would yield approximately $100 billion in its first year. CBO projected that federal revenue would total $3.5 trillion in FY2019.
Policymakers would face challenging decisions regarding the distribution of the new carbon tax revenues. Congress could apply revenues to support a range of policy objectives but would encounter trade-offs among the objectives. The central trade-offs involve minimizing economy-wide costs, lessening the costs borne by specific groups—particularly low-income households and displaced workers in certain industries (e.g., coal mining)—and supporting other policy objectives.
A primary argument against a carbon tax regards it potential economy-wide impacts, often measured as impacts to the U.S. gross domestic product (GDP). Some may argue that projected impacts should be compared with the climate benefits achieved from the program as well as the estimated costs of taking no action. The potential impacts would depend on a number of factors, including the program's magnitude and design and, most importantly, the use of carbon tax revenues.
In general, economic literature finds that some of the revenue applications would reduce the economy-wide costs from a carbon tax but may not eliminate them entirely. In addition, some studies cite particular economic modeling scenarios in which certain carbon tax revenue applications produce a net increase in GDP compared to a baseline scenario. These scenarios involve using carbon tax revenues to offset reductions in other tax rates (e.g., corporate income or payroll taxes). Although economic models generally indicate that these particular revenue applications would yield the greatest benefit to the economy overall, the models also find that lower-income households would likely face a disproportionate impact under such an approach. As lower-income households spend a greater proportion of their income on energy needs (electricity, gasoline), these households are expected to experience disproportionate impacts from a carbon tax if revenues were not recycled back to them in some fashion (e.g., lump-sum distribution).
A price on GHG emissions could create a competitive disadvantage for some industries, particularly "emission-intensive, trade-exposed industries." Policymakers have several options to address this concern, including establishing a "border carbon adjustment" program, which would levy a fee on imports from countries without comparable GHG reduction programs. Alternatively, policymakers could allocate (indefinitely or for a period of time) some of the carbon tax revenues to selected industry sectors or businesses. Relatedly, a carbon tax system is projected to disproportionately impact fossil fuel industries, particularly coal, and the communities that rely on their employment. To alleviate these impacts, policymakers may consider using some of the revenue to provide transition assistance to employees or affected communities.
The U.S. Fourth National Climate Assessment, released in 2018, concluded that "the impacts of global climate change are already being felt in the United States and are projected to intensify in the future—but the severity of future impacts will depend largely on actions taken to reduce greenhouse gas [GHG] emissions and to adapt to the changes that will occur."1 Although a variety of efforts seeking to reduce GHG emissions are currently underway on the international2 and sub-national level,3 federal policymakers and stakeholders have different viewpoints over what to do, if anything, about future climate change and related impacts. Their views regarding climate change cover a wide range of perspectives.4
For example, some contend that climate change poses a "direct, existential threat"5 to human society and that nations must start making significant reductions in GHG emissions in order to avoid "dire effects."6 To support this argument, proponents of climate change mitigation highlight the evidence and conclusions from recent reports that are generally considered authoritative, including:
On the other hand, some question whether there are sufficient risks of climate change to merit a federal program requiring GHG emission reductions.9 In addition, others argue that a unilateral approach to climate change by the United States could disproportionately impact domestic industries while achieving minimal results in global climate change mitigation.10
If Congress were to consider establishing a program to reduce GHG emissions, one option would be to apply a tax or fee on GHG emissions or the inputs that produce them. This type of approach is commonly called a carbon tax or a GHG emissions fee (see "Terminology Issues: A Carbon Tax or an Emissions Fee?").
Terminology Issues: A Carbon Tax or an Emissions Fee? In the context of carbon price policy, terminology may be a key issue. As many policymakers, stakeholders, and academic journals use the term carbon tax, this is the default term in this report. Related terms cited in economic literature include emissions fee or emissions charge. Several proposals in recent Congresses described their approach as a GHG emissions fee. Whether the policy proposal is labeled as a tax, fee, or other term, the carbon price may apply only to carbon dioxide (CO2) emissions or multiple GHG emissions. The choice of terminology between a tax and fee may have procedural consequences, particularly in terms of congressional committee jurisdiction. For instance, a carbon tax proposal may involve a referral to the House Committee on Ways and Means (in addition to any other House committees of jurisdiction). In the Senate, tax measures are referred to the Committee on Finance. Standing committees of the House, other than the Appropriations and Budget Committees, may report legislation creating or modifying user fees.11 Committees with jurisdiction over environmental policy (e.g., House Committee on Energy and Commerce and Senate Committee on Environment and Public Works) may have different perspectives, expertise, or policy objectives than tax committees. These differences could potentially influence the design of a carbon price instrument. In addition, there may be legal considerations depending on whether the program is structured as a fee or tax. These issues are beyond the scope of this report. |
This report does not compare and analyze the multiple policy tools available to Congress that could address climate change (see text box "Other Policy Options for Addressing GHG Emissions"). This report focuses on the policy considerations and potential impacts of using a carbon tax or GHG emissions fee to control GHG emissions.
The key human-related GHG is CO2, which is generated primarily through the combustion of fossil fuels: coal, oil, and natural gas. In 2016, fossil fuel combustion accounted for 94% of U.S. CO2 emissions and 76% of U.S. GHG emissions.12 A carbon tax could apply either directly to GHG emissions or to the materials—based on their carbon contents—that ultimately generate the emissions (i.e., "emissions inputs").13 A carbon price on emissions or their emissions inputs—mainly fossil fuels—would increase the relative price of the more carbon-intensive energy sources,14 particularly coal. This result could spur innovation in less carbon-intensive technologies (e.g., renewable energy, nuclear power, carbon capture and sequestration [CCS]) and stimulate other behavior that may decrease emissions, such as efficiency improvements. The energy price increases could also have both economy-wide impacts and negative effects on specific industries and particular demographic groups.
A carbon tax approach has received some attention and debate in recent years. In the 115th Congress, Members introduced nine carbon tax or fee proposals.15 Outside of Congress, the Climate Leadership Council—a bipartisan group of former policymakers and industry leaders—published a conceptual carbon tax approach in 2017 that generated some interest.16 Some of the industry leaders on the council represent major energy companies, including Shell, BP, and ExxonMobil.
Other Policy Options for Addressing GHG Emissions For policymakers considering actions to address climate change, a variety of policy instruments are available. Another option for directly reducing GHG emissions is to impose an emissions cap, likely complemented with an emissions trading program (i.e., cap-and-trade). To some extent, a carbon tax and cap-and-trade program would produce similar effects: Both would place a price on carbon, both could increase the price of fossil fuels, and both could reduce GHG emissions. Preference between the two approaches ultimately depends on which variable policymakers prefer to more precisely control—emission levels or emission prices. As a practical matter, these market-based policies may include complementary or hybrid designs, incorporating elements to increase price certainty or emissions quantity certainty. For example, legislation could provide mechanisms for adjusting a carbon tax if a targeted range of emissions reductions were not achieved in a given period. Alternatively, legislation could include mechanisms that would bound the range of market prices for emissions allowances to improve price certainty. Although recent attention has largely focused on market-based mechanisms such as a carbon tax and cap-and-trade programs, nonmarket policy tools may be an option to address some emission sources. For example, Congress has already addressed emissions from cars, light trucks, and government buildings through performance standards. In addition, Congress may continue to support the development of GHG emission mitigation technologies, such as CCS, or as a supplement to the primary climate change mitigation policy.17 |
On the other hand, many Members have expressed their opposition to a carbon tax. Starting in the 112th Congress and going through the 115th Congress, Members have introduced resolutions in both the House and Senate expressing the view that a carbon tax is not in the economic interests of the United States. In 2018, the House passed a resolution "expressing the sense of Congress that a carbon tax would be detrimental to the United States economy" (H.Con.Res. 119).18 An analogous resolution was not introduced in the Senate in the 115th Congress.
The first section of this report examines carbon tax design issues, including the point of taxation, the rate of taxation, and potential border carbon adjustments. The second section discusses issues related to the distribution of carbon tax revenues. The third section discusses additional considerations associated with a carbon tax program, including estimates of GHG emissions, federal revenue, and fossil fuel prices and changes in energy use. The fourth section provides concluding observations.
If policymakers decide to establish a carbon tax system, Congress would face several key design decisions, including the point of taxation—where to impose the tax and what to tax—the rate of taxation, and whether and/or how to address imported carbon-intensive materials.
Alternatively, Congress could direct one or more federal agencies to determine these design features through a rulemaking procedure. Although a few of the GHG emission reduction proposals in prior Congresses delegated such authority to an agency, such as the U.S. Environmental Protection Agency (EPA),19 all of the proposals since the 111th Congress have included some degree of design details in the statutory language. (A later section discusses carbon tax revenue application considerations.)
The point of taxation would determine which entities would be required to (1) make tax payments based on emissions or emission inputs, such as fossil fuels, (2) monitor emissions or emission inputs, and (3) maintain records of relevant activities and transactions. This section provides some considerations for policymakers deciding which GHG emissions and/or emission sources to cover in a carbon tax system.
Throughout the U.S. economy, millions of discrete sources generate GHG emissions: power plants, industrial facilities, motor vehicles, households, commercial buildings, livestock, etc. Administrative costs and challenges would likely increase with a broader scope of an emissions tax.
A carbon tax may apply to CO2 emissions alone, which account for most U.S. GHG emissions, or to multiple GHGs. Carbon tax proposals that apply only to CO2 generally attach a price to a metric ton of CO2 emissions (mtCO2). Some sources emit non-CO2 GHGs, such as methane, nitrous oxides, and sulfur hexafluoride. GHG emissions from these sources could be addressed by attaching a price to a metric ton of CO2 emissions-equivalent (mtCO2e). This term of measure is used because GHGs vary by global warming potential (GWP). At these sources, the determined GWP values would be an important issue.20
Policymakers may consider limiting the tax to sectors or sources that emit above a certain percentage of total U.S. GHG emissions, many of which currently report their emissions to the government. For more than 20 years, monitoring devices or systems have been installed in smokestacks of most large facilities, such as power plants, which are required to periodically report emissions data to EPA.21 In addition, since 2010, EPA has collected annual emissions data from approximately 8,000 facilities that directly release above certain amounts of GHG emissions.22 Using these established monitoring frameworks, policymakers could employ a "downstream" approach, applying a carbon tax at the point where the GHGs from these facilities are released to the atmosphere.
Alternatively, the tax could be applied to reliable proxies for emissions, such as emission inputs. For example, the carbon content of fossil fuels—coal, natural gas, petroleum—can serve as a proxy for the emissions released when the fuels are combusted.23 Applying a tax on emission inputs allows for the consideration of various points of taxation. For instance, emission inputs could be taxed at "upstream" (e.g., wells) or "midstream" stages in that process (e.g., refineries), the latter allowing for potential tax administration advantages that may be provided by specific infrastructure chokepoints in the fossil fuel market. For example, with respect to petroleum, the number of upstream sources—wells that produce crude oil—is over 445,000, but the number of midstream sources—facilities that refine crude oil—is only 137.
Table A-1 (in Appendix A) lists the top GHG emission sources in the United States. These sources combined to account for approximately 95% of U.S. GHG emissions in 2016. Table A-1 identifies the number of entities for each source category (e.g., number of coal mines, number of steel production facilities) and the percentage of total U.S. GHG emissions the category contributes.
In the case of fossil fuel combustion—which accounted for 76% of total U.S. GHG emissions—the table provides several options for segmenting the universe of sources if policymakers choose to implement a carbon tax. It identifies the number of entities that might be subject to the carbon tax under a particular option (pending any exclusions). For example, policymakers could address fossil fuel combustion emissions by applying a carbon tax to fossil fuels (based on their carbon content) at the following entities, which include both upstream and midstream infrastructure chokepoints:
Some of the above points of taxation might take advantage of the administrative frameworks for existing federal excise taxes. For example, a per-barrel federal excise tax on crude oil at the refinery supports the Oil Spill Liability Trust Fund.25 An excise tax on the sale or use of coal supports the Black Lung Disability Trust Fund.26
A central policy choice when establishing a price on GHG emissions is the rate of the carbon tax. Several approaches, which are discussed below, could inform the decision.
One approach would set the carbon tax rate at a level or pathway—based on modeling estimates—that would achieve a specific GHG emissions target. For example, a 2018 study estimated the carbon tax rate needed to meet the U.S. GHG emission reduction targets established under the 2015 Paris Agreement: 26%-28% below 2005 net GHG emission levels by 2025.27 The study found that a constant tax rate of $43/ton starting in 2019 would meet the 2025 reduction target.28
Emissions reduction estimates from carbon tax programs are based on multiple assumptions. Accordingly, such estimates provide different tax rates needed to meet a particular emissions target depending on these assumptions.29 See "Impacts on GHG Emission Levels" for selected analyses of emission reductions for a given carbon price and rate of price increase.
Under another approach, policymakers could base the carbon tax rate on the estimated marginal30 net benefits associated with reduced CO2 emissions.31 The net benefits would be the avoided net damages (i.e., costs) of climate change.32 The estimates of net benefits of avoided emissions often rely on analyses of the social cost of carbon (SC-CO2) or the social cost of greenhouse gases (SC-GHG).33 Therefore, policymakers could use SC-CO2 measurements—as the basis for an estimate of the net benefits of a marginal change in emissions—to set the rate of a carbon tax or emissions fee.34
One potential challenge of relying on SC-CO2 estimates to set a carbon fee are methodological concerns.35 For example, the existing estimates in peer-reviewed research cover a wide range. In addition, some argue that the underlying simulation models for estimating the SC-CO2 values are insufficient. For any level of emissions, the projected increase in global average temperature may cover multiple degrees Fahrenheit, and other measures of climate change, such as precipitation patterns, may encompass directional uncertainties. No estimates of impacts are comprehensive at this time, and many of the risks are difficult to estimate and value.
When valuing the SC-CO2, analysts encounter a range of views on methods and assumptions, and establishing study parameters may be challenging. For example, estimates of the monetary values of climate change impacts may be difficult or controversial to estimate, such as the monetary values associated with human deaths or sickness. A related framework question is whether to include global climate impacts or just domestic impacts.36
In addition, the element of time in climate change impacts particularly complicates the valuation. The fact that many impacts of climate change will occur in the distant future requires consideration of society's willingness to pay in the near term to reduce emissions that would cause future damages, mostly to future generations. To take time into account, economists discount future values to a calculated "present value." Economists do not agree on the appropriate discount rate(s) to use for a multi-generational, largely nonmarket issue such as human-induced climate change. The choice of discount rate can significantly increase or decrease values of the SC-CO2. A low discount rate would give greater value today to future impacts than would a higher discount rate. High discount rates can reduce the value today of future climate change impacts to a small fraction of their undiscounted values. A high discount rate would recommend applying fewer of today's resources to addressing climate change impacts in the future.
Since 2008, federal agencies have used SC-CO2 estimates in dozens of final rulemakings as a method to estimate the net benefits of abating CO2 emissions.37 An Interagency Working Group prepared SC-CO2 estimates, which were updated over time and subjected to expert and public comment. On March 28, 2017, President Trump issued Executive Order 13783, "Promoting Energy Independence and Economic Growth," which effectively withdrew the federal SC-CO2 estimates. Nonetheless, federal agencies have used new, interim values generated by EPA in 2017, modified from the withdrawn technical support documents, in regulatory and other decisions. Legislation could set a carbon price citing any of these SC-CO2 values or others available from nonfederal researchers or prescribe methods for estimating new ones.
Using SC-CO2 estimates to set the tax rate would involve a cost-benefit framework. Although many posit that a cost-benefit framework remains the best option,38 some economists argue that a cost-benefit framework may be inappropriate for climate change policy for these reasons39
Policymakers might consider a carbon tax as a fiscal tool to help reduce the federal deficit, reduce other taxes, or pay for specific programs that may or may not be related to climate change policy. In addition, some have proposed a phased-in approach, setting a rate that is initially lower but increases at an announced or adjustable rate either for a fixed period or indefinitely. Advantages of this approach include providing an opportunity for consumers and investors to adjust their behavior before the higher tax rates go into effect, such as purchasing more energy efficient appliances or investing in low-emissions technologies. Phasing in a carbon tax, however, could delay climate-related benefits.
If Congress finds agreement in principle on carbon pricing, the rate(s) could emerge from the process of reaching political agreement. Elements that might be considered include the options described above or consideration of the magnitude of overall economic impact; impacts on certain economic sectors, regions, or population groups; timing to motivate and allow an orderly transition to a lower-GHG economy; or other factors.
Many stakeholders have voiced concerns over how a U.S. carbon price system would interact with policies in other nations, particularly if the United States were to enact a carbon tax system that covers more sources or is more stringent than enacted elsewhere. A central concern is that a U.S. carbon tax could raise U.S. prices more than the prices of goods manufactured abroad, potentially creating a competitive disadvantage for some domestic businesses.42 Certain businesses may become less profitable, lose market share, and reduce jobs.
The industries generally expected to experience disproportionate impacts under a U.S. carbon tax are often described as "emission-intensive, trade-exposed" industries. An industry's CO2 emission intensity is a function of both direct CO2 emissions from its manufacturing process (e.g., CO2 from cement or steel production) and indirect CO2 emissions from the inputs to the manufacturing process (e.g., electricity, natural gas). Such industries are likely to experience greater cost increases than less carbon intensive industries, all else being equal. In general, trade-exposed industries are those that face greater international competition compared to other domestic industries. A carbon tax could present a particular challenge for these industries, because they might be less able to pass along the tax in the form of higher prices, because they may lose global market share—and jobs—to competitors in countries lacking comparable carbon policies.
Policymakers might consider approaches to mitigate these potential economic impacts in several ways. One approach that has received interest in recent years is a border adjustment mechanism, which is often described as a border carbon adjustment (BCA) in the carbon tax context. A BCA would apply a tariff to emission-intensive, imported goods such as steel, aluminum, cement, and certain chemicals. Each of the carbon price proposals in the 115th Congress would have established a BCA to address emission-intensive imports.43
Another rationale for adding a BCA to a carbon tax system is the possibility that it would encourage other nations to adopt comparable carbon price policies.44 Many of the recently proposed BCA mechanisms allow for exemptions for nations with comparable programs.
To date, no nations have implemented a BCA as part of their climate change policies. Establishing an economically efficient BCA would likely present substantial challenges.45 For example, policymakers must decide which goods and/or industries would be covered by a BCA and how the adjustment program would assess the comparability of varied climate-related policies in other nations. In addition, accurately determining and verifying the volume of GHG emissions embodied in a particular imported product would be data intensive and challenging. To alleviate some of the measurement complexity, policymakers could limit the program to selected industries and apply default values and assumptions to particular manufacturing processes. However, this simplified approach could result in less accurate import price adjustments, which could potentially affect the accuracy of GHG emission reductions achieved by the carbon tax program.46 Another option would be to allow companies to provide measured, independently verified emissions data as an alternative to default values.
In addition, the border adjustment approach would likely raise concerns of violating international trade rules.47 Further, some researchers have highlighted the potential for unintended consequences from a BCA. For example, some studies have found that a border adjustment may lead to lower net exports than the carbon price alone, due to the adjustment's terms-of-trade effect on U.S. currency.48 These issues are beyond the scope of this report, but some of the concerns may be lessened to some degree if a larger number of nations establish comparable emission reduction policies, as many have agreed to do under the Paris Agreement.49
Another possible rationale for a BCA is to address the concern of "emissions leakage" (or "carbon leakage"). Emissions leakage "occurs when economic activity is shifted as a result of the emission control regulation [e.g., a carbon tax program] and, as a result, emission abatement achieved in one location that is subject to emission control regulation is [diminished] by increased emissions in unregulated locations."50 The concern of emissions leakage has been central in the debate over whether the United States (or any nation) should unilaterally address GHG emissions. A BCA may diminish the potential for emissions leakage by reducing the incentive to shift economic activity to a nation without a comparable carbon tax. However, some recent studies raise questions regarding the degree to which emissions leakage would be a concern under a unilateral U.S. carbon tax.51
Although a tax may be levied on fossil fuels or GHG emission sources at various points in the economy, the carbon tax impacts may be experienced elsewhere.52 Policymakers have multiple options to address these expected impacts. Policymakers would face challenging decisions regarding the distribution of the new carbon tax revenues. As discussed below, some economic analyses indicate that certain distributions of tax revenue—depending on the level of the tax—would have a greater economic impact than the direct effects from the tax or fee on GHG emissions.53
Carbon tax revenues could be treated as general fund revenue without a dedication to a specific purpose in the enacting legislation (i.e., subject to the annual appropriations process), or policymakers could state that the new revenues would support deficit (or debt) reduction. Alternatively, the enacting legislation could return the tax revenue to the economy in some manner, sometimes called "revenue recycling." All of the carbon tax legislative proposals in recent Congresses have proposed some manner of revenue recycling, specifically directing the carbon tax revenue to support specific policy objectives.54
Carbon tax revenues may be used to support a variety of policy goals. When deciding how to allocate the new revenue stream, policymakers would likely encounter trade-offs among objectives, including:
In general, economic carbon tax studies have found that the relative ranking of revenue recycling options to mitigate the economy-wide impacts is generally the opposite of the relative ranking for alleviating distributional impacts. The contrasting relative rankings highlight a central tradeoff policymakers would face when deciding how to allocate carbon tax revenues.
The following sections discuss these trade-offs and some of the revenue application options that have received attention in recent years. A large body of economic literature has examined the economic impacts of hypothetical carbon tax programs, particularly the impacts of using the carbon tax revenues for different purposes. Many of the economic studies cited below were prepared prior to the enactment of the Tax Cuts and Jobs Act (TCJA, P.L. 115-97). Signed by President Trump in December 2017, the act changed various elements of the U.S. federal tax system.55 In particular, the act lowered the corporate income tax rate from 35% to 21%. As discussed below, adjusting the corporate income tax rate is one of the central policy options generally considered in carbon tax economic literature both before and after enactment of P.L. 115-97. Based on a selected review of the economic literature that includes the tax code changes in P.L. 115-97, the central conclusions from carbon tax literature regarding revenue recycling appear to be largely unchanged.56
Economic Analyses Typically Do Not Include Policy Benefits In general, carbon tax analyses do not consider the benefits that would be gained by reducing GHG emissions and avoiding climate change and its adverse impacts. Rather, most examine only the cost side of a cost-benefit analysis. This is largely because most economic models are structured to simulate markets and goods and services valued in markets, not effects on human health, species, and the environment. In addition, carbon tax analyses generally do not include potential ancillary benefits that reduced GHG emissions could provide. For example, a reduction in GHG emissions from certain sectors may entail a reduction in hazardous air pollutants, which could provide health-related benefits.57 Typically, when this and many other reports discuss the "costs" of a policy, costs refer only the gross costs and not the net costs taking into account the benefits of the policy. If a carbon tax's benefits were to exceed its costs, the policy would have net benefits. Net costs or benefits could not be determined without analysis that fully includes benefits. In addition, the potential benefits of GHG emissions reduction may not accrue to the entities that bear the costs of the carbon tax. Scientists and economists generally examine and monetize the costs of climate change—alternatively, the benefits of reducing GHGs—separately from specific carbon price policy proposals. For example, a 2015 report from EPA estimated the physical and monetary benefits to the United States of reducing global greenhouse gas emissions.58 |
A primary concern with a carbon tax is the potential economy-wide costs that may result.59 Generally, a tax or fee on GHG emissions or the fuels that generate them would increase certain energy prices, namely fossil fuels, in the near- to medium-term as well as the prices of goods and services produced using these materials, like electricity. This outcome is inherent to the carbon tax, as its purpose is to increase the relative price of the more carbon-intensive energy sources compared to less carbon-intensive alternatives, encourage innovation in less carbon-intensive technologies, and promote other activity (e.g., energy efficiency) that may decrease emissions. These expected outcomes will have some economy-wide impacts.
Ultimately, the economy-wide effects would depend on a number of factors, including, but not limited to, the magnitude and scope of the carbon tax and, most importantly, use of the ensuing revenues. Economy-wide costs (referred to as macroeconomic costs) are often measured in terms of changes in projected gross domestic product (GDP) or another societal-scale metric, such as economic welfare.60 The magnitude of macroeconomic impacts from a carbon tax has been a subject of debate among policymakers and stakeholders. In addition, results of economy-wide impacts will not include comparisons of impacts to different subpopulations or geographic regions, which may be of interest to policymakers.
Multiple economic studies and models have examined and compared various options for addressing the economy-wide impacts that may result from a carbon tax. One option for reducing the economic cost of a carbon tax is using the revenue to reduce existing taxes, such as those on labor, income, and investment. Economists generally describe such taxes as distortionary, because the taxes discourage economically beneficial activity, such as employment and investment.
Another option for policymakers is to use the tax revenues to address the national debt. Fewer studies have examined deficit reduction scenarios, because "modeling the effects of budget deficits is much more difficult than modeling the effects of tax cuts."61 Some studies have concluded that using tax revenues for this purpose would help alleviate economy-wide costs from a carbon tax because of the reduced need to impose distortionary taxes in the future.62 These studies indicate that the economy-wide benefit would be delayed and its realization assumes policymakers would, sometime in the future, address the deficit by raising taxes.
Many recent legislative proposals would distribute the carbon tax revenue back to households in lump-sum payments. Policymakers have generally included this carbon tax revenue application to address distribution impacts (discussed below). These payments could take multiple forms. Economic analyses typically assume an equal payment to individuals or households regardless of their income or location or the effects of the carbon price on them individually. Alternatively, payments could be targeted or scaled to different segments of the population.
Among the options mentioned above, economic studies indicate that using carbon tax revenues to offset reductions in existing, distortionary taxes would be the most economically efficient use of the revenues and yield the greatest benefit to the economy overall. This concept is sometimes referred to as a "tax swap."
Using carbon tax or fee revenues to offset other distortionary taxes (e.g., labor or capital) may yield a "double-dividend,"63 which includes:
The economic models that examine the economic impacts of a carbon tax differ in their frameworks and underlying assumptions and often include multiple scenarios involving different uses of carbon tax revenue. In general, the economic models find that certain revenue recycling options may reduce the economy-wide carbon tax impacts but may not eliminate them entirely.64
Some studies cite particular economic modeling scenarios in which a carbon tax with certain revenue recycling applications would produce a net increase in GDP or economic welfare compared to a baseline scenario.65 These results indicate that, in certain modeling conditions, the economic improvements gained by reducing existing distortionary taxes would be greater than the costs imposed by the new carbon tax (without including the intended climate benefits of the policy). For example, results from a 2018 study demonstrated a net increase in GDP, compared to baseline conditions,66 when carbon tax revenues were used to finance proportionate reductions in labor tax rates (payroll tax).67
In general, the economic carbon tax studies usually agree on the relative ranking of revenue recycling options in terms of their ability to mitigate the economy-wide impacts of a carbon tax program. The studies indicate that the approaches that use carbon tax revenue to proportionately lower existing tax rates are able to mitigate more of the carbon tax economy-wide costs than using the revenue to provide a lump-sum distribution to individuals or households.
Researchers prepared multiple carbon tax analyses prior to the enactment of the TCJA in 2017 that estimated the magnitude GDP impacts.68 As with other estimates relating to carbon tax impacts, the results depend on the scope of the carbon tax, underlying assumptions in the analytical model, and the terms of measurement: Some estimates measure GDP growth rates; others measure actual GDP.
Figure 1 illustrates the modeled GDP results from a 2018 carbon tax analysis that includes the changes made by the TCJA. This study assessed the GDP impacts under a $50/mtCO2e carbon tax (starting in 2020 and increasing by 2% annually) that would apply to CO2 emissions from fossil fuel combustion and methane emissions from fossil fuel production activities.69 The figure compares projected GDP impacts under a baseline scenario (i.e., no carbon tax) with three carbon tax revenue applications: a payroll tax rate reduction tax swap, a lump-sum distribution to households, and a scenario that would use tax revenue to reduce the national debt for 10 years and then use revenues for a lump-sum distribution to households. The figure projects GDP impacts in 2020, 2024, 2029, and 2039.
As the figure indicates, the payroll tax rate scenario would result in a 0.1% loss of GDP in the first year (2020), but would yield GDP gains in subsequent years compared to baseline. The lump-sum distribution approach would yield GDP losses each year, ranging from 0.3% to 0.4% below the projected baseline. The deficit reduction approach would yield a range of GDP losses in the first 10 years—ranging from 0.4% to 0.04%—but would yield a GDP gain in 2039 (if not before), compared to baseline.
Opponents of a carbon tax approach often highlight the GDP losses that would result from a carbon tax.70 Policymakers and stakeholders may have different perspectives regarding whether the magnitude of the GDP impacts are significant. In addition, GDP impact estimates may be presented in several ways. For example, one could compare the differences in GDP value for a particular year between carbon tax scenarios and a baseline scenario. This approach is employed in the above figure. Alternatively, one could present the GDP losses with a cumulative measure. For instance, if one were to add up the annual GDP losses (for example, over a 10-year period) from the lump-sum scenario compared to the baseline scenario, the resulting sum would be much larger. These types of calculations would require assumptions about annual GDP growth rates.
Some may point out that the GDP impact estimates do not account for the environmental and public health benefits for reducing GHG emissions and that the GDP projections should be compared with the climate benefits achieved from the program as well as the estimated costs of taking no action. As discussed above, estimates of climate-related benefits and costs often contain considerable uncertainty and have generated debate in recent years.
Many economic analyses have found that a carbon tax (before revenue recycling) would produce a regressive outcome among households, with lower-income households facing a larger impact from the tax than higher-income households.71 However, "the degree to which a carbon tax is found to disproportionately burden low-income households varies across studies, based on the metrics against which analysts measure costs."72
Entities that pay the carbon tax may pass its costs back to fuel producers or forward to fuel consumers. If entities pass the costs forward, consumers would face higher prices for fuels and electricity and carbon-intensive products. When the carbon tax is passed forward to consumers, lower-income households in particular would likely face a disproportionate impact (i.e., regressive outcome), because a larger percentage of their income is used to pay for energy needs, such as electricity, gasoline, or home heating oil.
Many economic analyses of carbon price scenarios assume that the vast majority (if not all) of the carbon tax impact is passed forward to consumers, leading to a regressive outcome.73 On the other hand, if entities pass the costs backward to producers, the tax impacts would fall on labor through reduced wages or owners of capital through reduced returns on investment.74 Economic models that assume this outcome produce more progressive results (absent revenue recycling), with lower-income households experiencing smaller impacts than higher-income households.75
The economic analyses appear to agree that the distributional effects among households (i.e., regressive vs. progressive) of a carbon tax program would be largely dependent on how the carbon tax revenues were used.76 A number of economic studies have used models to estimate the impacts of a carbon tax across households under several revenue distribution scenarios.77 The results vary because the studies use different modeling frameworks, carbon tax rates and scopes, underlying assumptions, and ways to measure impacts.78
For example, a 2018 study assessed the impacts to household income for different household quintiles under a carbon tax of $50/mtCO2e, starting in 2020.79 This study examined four revenue distribution scenarios:
This report highlights this study, because it includes carbon tax revenue applications that have generated interest in recent years. In addition, this analysis was prepared after the 2017 tax rate changes in P.L. 115-97.
Figure 2 illustrates the modeled results, which the study measured as percentage reductions to household income. Thus, negative percentages illustrated in the figure are gains to household income. The per-capita rebate approach provides the most progressive result, yielding a net benefit for the bottom three household quintiles but a net loss for the top quintile. The fourth quintile impact is zero. By comparison, the other approaches produce varying degrees of regressive outcomes while providing a net gain for wealthier groups in two particular instances. Of the four options, the payroll tax rate reduction approach estimates the smallest variance between the income quintiles, ranging from a 0.5% loss for the lowest quintile to a 0.2% gain for the fourth quintile. The fifth quintile impact is zero.
The relative ranking among options for progressivity is generally the opposite of the relative ranking for mitigating economy-wide impacts. Other economic analyses have found similar relative rankings of revenue recycling options.80 The contrasting rankings highlight a central tradeoff policymakers would face when deciding how to allocate carbon tax revenues.
Policymakers could allot some portion of the revenues to partially support both objectives. In a 2018 carbon tax study, economic modelers assessed a scenario in which a portion of the revenue was used to offset the welfare impacts for the lowest-income household quintile and the remaining revenue supported reductions in capital tax rates.81 The study's models estimated that a carbon tax's impacts on the lowest-income household quintile could be counteracted with approximately 10% of the revenue. This would allow for 90% of the revenue to be used to reduce capital tax rates and thus address the economy-wide impacts from the carbon tax.
As discussed above, a carbon tax is projected to disproportionately impact certain industries, particularly those that are described as "emission-intensive, trade-exposed industries." To address these concerns, many of the recent carbon tax legislative proposals have included design mechanisms that would attach a carbon price to certain imported materials and products (see "Border Carbon Adjustments").
Another approach to addressing the competitiveness concerns of domestic industries would involve distributing a portion of the carbon tax revenues to emission-intensive, trade-exposed industries as rebates based on their output.82 Output rebate proposals generally determine rebate amounts by measuring emissions intensity at the relevant sector level or by a benchmark that would encourage facilities to reduce their emissions intensity.83 These rebates could be phased out over time or continue until other nations adopt comparable carbon price policies. Under a carbon tax system in Canada, which is scheduled to take effect in 2019, industries will be subject to an "output-based pricing system."84 Some contend that the data and administrative resources necessary to implement such a program would be substantial.85
A carbon tax system is also expected to disproportionately impact fossil fuel industries and the communities that rely on their employment. In particular, coal-mining communities are expected to experience substantial impacts based on the coal production declines predicted in carbon tax analyses. For example, one model estimates that under a $50/mtCO2e carbon tax, annual U.S. coal production would decline by almost 80% in 2030 compared to a reference case.86 Policymakers may consider supporting worker transition or community transition assistance to help mitigate the economic impacts.87 Several of the recent carbon tax proposals would have devoted carbon tax revenues for this objective.88
Policymakers may also consider using the carbon tax revenues to provide funding to support a range of objectives, which may include policy goals that are not directly related to climate change. Some options are identified below, and many have been included in recent legislative proposals or in state GHG mitigation programs that raise revenues:
Allowance Value Distribution in RGGI and California's Cap-and-Trade Programs Both the RGGI—a coalition of nine states from the Northeast and Mid-Atlantic regions—and California implement cap-and-trade programs to reduce GHG emissions. Analogous to carbon tax revenue decisions, one of the more controversial and challenging questions for policymakers when designing a cap-and-trade program is how, to whom, and for what purpose to distribute the emission allowances. The RGGI's cap-and-trade system took effect in 2009 and applies to CO2 emissions from electric power plants. RGGI states have answered the "how" question by employing auctions to distribute the vast majority of allowances, offering 91% of their budgeted emission allowances at auction between 2008 and 2016. As a group, RGGI states have distributed the vast majority of the emission allowance value to support energy efficiency, renewable energy, or other climate-related efforts or to provide financial assistance directly to households.91 California established a cap-and-trade program that took effect in 2013, covering multiple GHGs that account for approximately 85% of California's GHG emissions. In California, approximately 50% of emission allowances have been sold through an auction and 50% provided at no cost to various entities, including covered sources. Investor owned utilities (which received 16% of the allowances in 2016) are required to auction their allowances with the revenues supporting electricity consumers. California has used its cap-and-trade auction revenue to fund a variety of objectives, including a high-speed rail project, affordable housing, and low-carbon vehicles, among other programs.92 |
Multiple economic studies have estimated the emission reductions that particular carbon tax designs could achieve. Economic models provide estimates based on the best information available at the time. Comparing results from different studies is problematic, because the studies' scenarios differ in multiple ways, including the tax rate, start date, scope of the program, assumptions about economic growth and technological advances, and assumptions about other federal and state policies and their effects.
A 2018 study avoided some of these comparison difficulties by inviting modeling teams to analyze a coordinated set of scenarios.93 The 2018 Stanford Energy Modeling Forum study ("EMF 32") assembled 11 modeling teams to analyze the economic impacts of four carbon tax scenarios starting in 2020: a $25/metric ton and $50/metric ton carbon tax, increasing annually by 1% and 5%.94 Within each of these carbon price frameworks, the models ran separate revenue distribution scenarios: a reduction in labor tax rates, a reduction in capital tax rates, and household rebates.
Figure 3 illustrates the study's estimates of CO2 emissions from fossil fuel combustion.95 The red lines in the figure display the average values for the 11 models. The shaded areas illustrate the range of results, highlighting the uncertainties in emission reduction estimates. Based on these results, the study authors concluded that each of the tax rate scenarios would likely achieve the U.S. CO2 emission reduction targets under the Paris Agreement.96
As Figure 3 indicates, a carbon tax or emissions fee could be set with the expectation that it would achieve an emissions reduction target, but the resulting level of emissions would be uncertain. The uncertainty of resulting emissions may lead some stakeholders to disfavor a carbon tax or fee option to control GHG emissions. Although uncertain emissions are inherent with a carbon tax approach, Congress could employ certain design elements to enhance the emission control certainty. For example, the existing GHG emission reporting data could be used to track the impact and performance of a carbon price.97 If policymakers determine that emission reduction is not occurring at a desired pace, the price could be amended. Legislation could establish the conditions and process by which price changes could occur.
Some may argue that adjusting the carbon price to reflect actual emissions performance would undermine the benefits of price certainty. Others may point out that unplanned adjustments to the carbon price could be politically unpalatable. For example, it may be difficult for policymakers to increase the tax rate, especially during periods of high energy prices. Some have suggested that Congress authorize an independent board or agency with the mandate to modify the tax rate administratively in order to meet pre-determined emission reduction objectives.98 Although this approach would likely improve emission certainty, long-term price certainty may be sacrificed to some degree, depending on the authority of the delegated entity to adjust the tax rate.
Some would argue that potential year-to-year emission variations under a carbon tax would not undermine efforts to control climate change so long as long-term emission goals are achieved. Indeed, they would assert that annual emission fluctuations are preferable to price volatility that could result from an emissions cap program. They support their preference for price control by suggesting that CO2 generates damages through its overall accumulation as concentrations in the atmosphere, not its annual flow.99
A potential concern of a carbon tax is whether it would be effective in reducing GHG emissions in all of its covered sectors, particularly emissions in the transportation sector. As of 2016, the transportation sector contributes the largest percentage (36%) of CO2 emissions from fossil fuel combustion, with electric power second at 35%.100 Carbon tax analyses generally agree that the majority of the emission reductions resulting from a carbon tax program would occur in the electricity sector. By comparison, economic models generally conclude that a carbon tax would have much less of an impact on emissions in the transportation sector.101 Several factors explain this projected outcome. The transportation sector offers fewer opportunities to switch to less carbon-intensive fuels in the short term than does the electric power sector, which can displace coal with natural gas relatively quickly. In addition, short-term emission changes in the transportation sector are largely influenced by changes in driving demand, which has historically been relatively insensitive to gasoline price increases.102
Based on these projected outcomes, some may contend that to achieve deeper, long-term reductions in total GHG emissions, policymakers would need to complement a carbon tax with other programs, such as vehicle technology standards (e.g., Corporate Average Fuel Economy, CAFE) or fuel performance standards, among other options.103
The quantity of revenues generated under a carbon tax system depend on the program's design features, namely the tax base and rate, as well as such independent factors as prices in global energy markets. They would also depend on how covered emission sources respond to the carbon price, for example by adopting alternative technologies or changing behavior. Several carbon tax studies have prepared revenue estimates, which are presented in Table 1.
From a public finance perspective, a carbon tax may not be a reliable source of long-term funding, because a primary goal of the carbon tax is to reduce its tax base—GHG emissions. The estimates in Table 1 project carbon tax revenue values in 2020. Multiple studies have projected carbon tax revenue trajectories beyond 2020. In the 2018 EMF 32 study,104 all but one of eight models projected carbon tax revenue increases from 2020 through 2040.105 The carbon tax scenarios with larger annual rate increases resulted in steeper trajectories of increasing revenues through 2040. The models' estimates of annual carbon tax revenue in 2040 ranged from approximately $250 billion to $475 billion (under the tax rate scenario of $50/metric ton, increasing 5% annually).106
Author (Year) |
Scope of Program |
Carbon Price |
Annual Revenue Estimates |
Congressional Budget Office (2018) |
Tax on CO2 emissions from energy-related activities and other selected GHG emission sources |
Tax would start in 2019 at $25/mtCO2e, increasing by 2% per year plus inflation |
$103 billion in 2020 |
EMF 32 Study (2018) |
Tax on CO2 emissions from fossil fuels |
Tax would start in 2020 at $25/mtCO2, increasing by 1% per year plus inflation |
Model results ranged from $100 million to $125 million in 2020 |
Tax would start in 2020 at $50/mtCO2, increasing by 1% per year plus inflation |
Model results ranged from $170 million to $240 million in 2020 |
||
Office of Tax Analysis (2017) |
Tax on CO2 emissions from energy-related activities and other selected GHG emission sources |
Tax would start in 2019 at $49/mtCO2e, increasing by 2% per year plus inflation |
$210 billion in 2020 |
McKibbin et al. (2017) |
Fee on CO2 emissions from energy-related activities |
Fees start in 2020 at $27/mtCO2, increasing by 5% per year |
$110 billion in 2020 |
Source: Congressional Budget Office, Options for Reducing the Deficit: 2019-2028, 2018; James R. McFarland et al., "Overview of the EMF 32 Study on U.S. Carbon Tax Scenarios," Climate Change Economics, 2018; John Horowitz et al., Methodology for Analyzing a Carbon Tax, Department of the Treasury, Office of Tax Analysis, 2017; Warwick McKibbin et al., The Role of Border Adjustments in a U.S. Carbon Tax, Brookings Institution, 2017.
Fossil fuels have a wide range of CO2 emission intensity (i.e., emissions per unit of energy). As illustrated in Figure 4, the CO2 emission intensity of coal is approximately 30% more than oil and approximately 80% more than natural gas. These emissions intensity differences would lead to different tax rates per unit of energy across different fuels in a carbon tax regime.
Figure 4. CO2 Emissions Per Unit of Energy Comparison of Selected Fossil Fuels |
Source: Prepared by CRS; data from EIA, "Carbon Dioxide Emissions Coefficients by Fuel," https://www.eia.gov/environment/emissions/co2_vol_mass.php. |
Carbon taxes could affect fuel prices in complex ways. The change in consumer fuel prices would likely not be the same as the price paid by the party directly subject to the tax. Actual price impacts for consumers would depend on multiple factors, including whether:
In addition, market participants such as electric power plant operators can avoid paying the increased costs by substituting fuels or technologies. Energy consumers may modify their behavior in the marketplace—energy conservation, consuming less or different products and services—to mitigate impacts from the increased prices.
Table 2 includes estimates of price increases on coal, crude oil, natural gas, home heating oil, and motor gasoline based on a carbon tax rate of $25/mtCO2 that applies CO2 emissions from fossil fuel combustion. As indicated in the table, a carbon tax would have the greatest impact on the price of coal due to coal's relatively high CO2 emissions intensity. By comparison, a carbon tax is expected to have less of an impact on the price of gasoline, increasing its price by 8%.
Table 2. Estimated Price Increases by Fuel from a Carbon Tax of $25/mtCO2 on CO2 Emissions from Fossil Fuel Combustion
Fuel |
Estimated Carbon Tax on Fuel by Volume or Weight |
Average Market Prices |
Estimated Percentage Price Increase from Carbon Tax |
Coal |
$45.00/short ton |
Surface mine: $23/short ton Underground mine: $57/short ton |
196% 79% |
Natural gas |
$1.25/mcf |
Residential: $11/mcf Commercial: $8/mcf Industrial: $4/mcf Electric power: $4/mcf |
11% 15% 31% 31% |
Crude oil |
$10.75/barrel |
Domestic first purchase: $63/barrel |
17% |
Home heating oil |
$0.20/gallon |
$3.10/gallon |
6% |
Motor gasoline |
$0.23/gallon |
$2.78/gallon |
8% |
Source: Prepared by CRS. CRS calculated the estimated price increases for each fuel by multiplying a carbon tax rate by the CO2 emissions intensities for each fuel. Given that carbon prices could affect fuel prices in complex ways, the actual price increases that result from the illustrative carbon taxes would depend on multiple factors. CRS generated fuel-specific emission intensities from the CO2 coefficients (i.e., CO2 emissions per quadrillion BTU) and thermal conversion factors (BTU per fuel unit) for each fuel. CO2 coefficients are from EIA, "Carbon Dioxide Emission Coefficients," 2016; thermal conversion factors from EIA, Monthly Energy Review, April 2018, Appendices A2 (crude oil), A3 (home heating oil and motor gasoline), A4 (natural gas), and A5 (coal). Average market prices (2013-2017) are from EIA, Monthly Energy Review, Table 9.1 (crude oil), Table 9.10 (natural gas), and Table 9.4 (motor gasoline); home heating oil from EIA, "Weekly Heating Oil and Propane Prices"; coal from EIA, Annual Coal Report, various years, Table 28. Average coal prices include data from 2012 to 2016.
Calculated emission intensities include:
Coal = 1.8 mtCO2/short ton of coal. This value represents the CO2 coefficient for coal (electric power sector) and the thermal conversion factor for coal consumption from the electric power sector. Surface mining accounted for 65% of total coal production in 2016. Underground mining accounted for 35%.
Crude oil = 0.43 mtCO2/barrel of oil. This value represents the CO2 coefficient for crude oil and the thermal conversion factor for "unfinished oil." Price reflects domestic first purchase price.
Home heating oil = 0.008 mtCO2/gallon of oil.
Natural gas = 0.055 mtCO2/thousand cubic feet (mcf) of natural gas. This value represents CO2 coefficient for natural gas ("weighted national average") and the thermal conversion factor for electric power sector.
Motor gasoline = 0.009 mtCO2/gallon of gasoline. This value represents the CO2 coefficient for "motor gasoline" and the thermal conversion factor for motor gasoline (conventional).
Economic models have projected how carbon prices would impact energy use, particularly the consumption of different fossil fuels and less carbon-intensive alternatives, such as renewables or nuclear power. For example, the 2018 EMF 32 study, which included results from 11 modeling groups, assessed how several carbon tax scenarios would impact energy consumption. Highlights of these models' results (compared to reference case scenarios) include the following:107
A carbon tax is one policy option to address U.S. GHG emission levels, which contribute to climate change and related impacts. Economic modeling indicates that a carbon tax would achieve emission reductions, the level of which would depend on which GHG emissions and sources are covered and the rate of the carbon tax.
A carbon tax would generate a new revenue stream. The magnitude of the revenues would depend on the scope and rate of the tax and multiple market factors, which introduce uncertainty in the revenue projections. A 2018 CBO study estimated that a $25/metric ton tax on CO2 emissions from energy-related activities and other selected GHG emission sources would yield approximately $100 billion in the first year of the program. To put this estimate in context, the CBO projected that total federal revenue would be $3.5 trillion in FY2019.109
Policymakers would face challenging decisions regarding the distribution of the new carbon tax revenues. Depending on the level of the tax, some economic analyses indicate that the distribution of tax revenue could yield greater economic impacts than the direct impacts of the tax. Some models indicate that the economic impacts are greatest in the early years of the carbon tax.
Policymakers could apply the tax revenues to support a range of policy objectives. When deciding how to allocate the revenues, policymakers would encounter trade-offs among objectives. The central trade-offs involve minimizing economy-wide costs, lessening the costs borne by specific groups—particularly low-income households—and supporting a range of specific policy objectives.
A primary concern with a carbon tax is the potential economy-wide costs that may result. The potential costs would depend on a number of factors, including the magnitude, design, and use of revenues of the carbon tax. In general, economic literature finds that some of the modeled revenue applications would reduce the economy-wide costs imposed by a carbon tax but may not eliminate them entirely.
Policymakers and stakeholders may have different perspectives regarding whether these estimated economy-wide costs (typically measured in terms of GDP loss) represent a significant concern. Some argue that the estimated economy-wide costs should be compared with the policy option of not establishing a carbon tax. This comparison is uncertain as carbon tax analyses do not generally consider the benefits that would be gained by reducing GHG emissions and avoiding climate change and its adverse impacts.
Some studies cite particular economic modeling scenarios in which a carbon tax and revenue recycling could produce a net increase in GDP or economic welfare, compared to a baseline scenario. These scenarios involve using carbon tax revenues to offset reductions in existing, distortionary taxes, such as corporate income or payroll taxes. Although the models indicate that these revenue applications would yield the greatest benefit to the economy overall, the models also find that lower-income households would likely face a disproportionate impact under such revenue applications. As lower-income households spend a greater proportion of their income on energy needs, these households are expected to experience disproportionate impacts from a carbon tax if revenues were not recycled back to them in some fashion, such as a lump-sum distribution. Carbon tax revenues that are used to offset the burden imposed on various sectors or specific population groups would not be available to support other objectives.
An additional concern with a carbon tax involves potential disproportionate impacts to "emission-intensive, trade-exposed industries." Policymakers could select among several options to address these concerns, either by establishing a border carbon adjustment program or allocating some of the carbon tax revenues to selected industry sectors based on an output-based metric. If other nations were to adopt comparable carbon price policies, this concern may be alleviated to some degree.
Relatedly, a carbon tax is projected to disproportionately impact fossil fuel industries, particularly coal, and the communities that rely on their employment. To alleviate these impacts, policymakers could allocate some of the carbon tax revenue to provide transition assistance to employees or affected communities.
Table A-1 identifies sources of GHG emissions that account for 0.5% or more of total U.S. GHG emissions. The sources are listed in descending order by their percentage contribution. CO2 emissions from fossil fuel combustion, which accounts for almost 76% of total U.S. GHG emissions, are broken down by fossil fuel type: petroleum, coal, and natural gas.110
The table identifies potential points in the economy at which a carbon tax could be applied. The table lists the approximate number of entities that would be involved with different tax applications. The number of entities listed is current as of the most recent data available and varies accordingly by category. See table notes for details.
The right-hand column of the table provides additional comments for some of the emission sources. In some cases the comments discuss potential opportunities for additional GHG emissions coverage at a particular source. In other cases, the comments address potential limitations of covering all of the emissions from a particular source.
Table A-1. Selected Sources of U.S. GHG Emissions and Options for Potential Applications of a Carbon Tax
Potential Tax Application Options |
||||||||
GHG Emission Source |
Percentage of Total U.S. GHG Emissions (2016)a |
Entities |
Number |
Additional Comments |
||||
CO2 from fossil fuel combustion |
|
|
||||||
-petroleum |
|
Petroleum Option 1 |
With this option policymakers could levy a tax on CH4 emissions from oil field operations, potentially increasing the covered percentage of total GHG emissions from 34% to 35%. |
|||||
|
Petroleum wellsb and |
approx. 445,000 wells |
|
|||||
|
Petroleum importersc |
166 |
||||||
Petroleum Option 2 |
||||||||
Petroleum refineriesd and |
137 |
|||||||
Petroleum importers |
166 |
|||||||
-coal |
|
Coal Option 1 |
With this option policymakers could levy a tax on coal mine CH4 emissions, potentially increasing the covered percentage of total GHG emissions from 20% to 21%. |
|||||
Coal minese and |
690 |
|||||||
Companies supplying imported coalf |
8 |
|||||||
Coal Option 2g |
This option would only address coal used by electric utilities. Thus this option's covered percentage of total GHG emissions would be 19% instead of the 20% from "Coal Option 1." |
|||||||
Coal-fired power plantsh and |
381 |
|||||||
Companies supplying imported coal |
8 |
|
||||||
-natural gas |
|
Natural Gas Option 1 |
|
With this option policymakers could levy a tax on CH4 emissions from "natural gas systems," potentially increasing the covered percentage of total GHG emissions from 23% to 25.5%. |
||||
|
Natural gas wellsi and |
approx. 564,000 wells |
|
|||||
|
Natural gas importersj |
|
|
|||||
|
Natural Gas Option 2k |
|
This option would cover 17%-19% of total GHG emissions (compared to the 23%-25% in "Natural Gas Option 1"), because a substantial portion of natural gas that is produced domestically does not pass through a natural gas processing facility before it reaches an end user (including exported natural gas). |
|||||
|
Natural gas processorsl and |
|
|
|||||
|
Natural gas importers |
|
|
|||||
|
Natural Gas Option 3m |
|
By combining entities reporting on EIA Form 176 with natural gas fractionators, this option would cover 100% of natural gas consumption (23% of total GHG emissions). In addition, the Form 176 entities report data that could be used to levy a tax on some portion of the emissions associated with "CH4 from natural gas systems," potentially increasing the covered percentage of total GHG emissions from 23% to 24%. |
|||||
|
Entities reporting on EIA Form 176, including: (1) interstate/intrastate pipelines; (2) natural gas distributors; and (3) field, well, or processing plants that deliver natural gas directly to end users |
|
|
|||||
|
Natural gas fractionatorsn |
|
|
|||||
Nitrous oxide from agricultural soilso |
|
Farmsp |
approx. 2.05 million |
A number of agricultural activities lead to N2O emissions, including certain soil management practices and the application of livestock manure or synthetic fertilizer. Policymakers could levy a tax on synthetic fertilizer sales to address N2O emissions from the use of synthetic fertilizers, thus covering approximately 1.0% of total U.S. GHG emissions. |
||||
CH4 from natural gas systems |
|
|||||||
-field production |
|
Natural gas wells |
approx. 564,000 |
If policymakers levy a tax at the wellhead, the tax could potentially cover all CH4 emissions that occur at the wellhead and downstream of the wellhead: 2.5% of total GHG emissions. |
||||
-processing |
|
Natural gas processors |
|
If policymakers levy a tax at processors, the tax could potentially cover all CH4 emissions at natural gas processors and CH4 emissions that occur downstream of the processor. It is uncertain what percentage of downstream CH4 emissions would be addressed, because approximately 30% of domestically produced natural gas bypasses processing facilities (discussed in "Natural Gas Option 2"). |
||||
-transmission and storage |
|
Pipeline systemsq |
|
If policymakers levy a tax at pipeline systems, the tax could potentially cover all CH4 emissions at the pipeline level and CH4 emissions that occur downstream. |
||||
-distribution |
|
Local distribution companiesr |
|
If policymakers levy a tax at natural gas local distribution companies (LDCs), the tax could potentially cover CH4 emissions at the LDC and any that may occur in the distribution system to end users. |
||||
Methane from livestock |
|
Cattle operationss |
approx. 913,000 |
|||||
Hydrofluorocarbons from the substitution of ozone depleting substancest |
|
Fluorinated gas manufacturers (14) and companies that import fluorinated gases (35)u |
|
If policymakers levy a tax on fluorinated gas manufacturers and importers, the tax would not cover fluorinated gases in existing equipment. Thus the percentage of coverage would be less than 2.4%. |
||||
Methane from landfills |
|
Municipal solid waste landfillsv |
|
EPA regulations have required larger landfills to address CH4 emissions since 1996. |
||||
CO2 from nonenergy fuel use |
|
These emissions would likely be covered by tax on fossil fuels (above)w |
||||||
Methane from petroleum systemsx |
|
Petroleum wells |
approx. 360,000 |
|||||
Methane from manure management |
|
Cattle operations Swine operationsy |
approx. 913,000 approx. 63,000 |
|||||
Methane from coal mines |
|
Underground coal mines (251) Surface coal mines (439)z |
|
In 2016, approximately 76% of these CH4 emissions were from underground mines, which ventilate the CH4 for safety reasons or capture the CH4 and sell it for energy use. Attaching a tax to emissions from surface mines may present more challenges. |
||||
CO2 from iron/steel production |
|
Raw steel production facilities Integrated steel millsaa |
|
|||||
CO2 from cement manufacturing |
|
Cement plantsbb |
|
|||||
Percentage of Total GHG Emissions |
|
Source: Prepared by CRS with specific data sources provided below. Some numbers subsets may not match the total numbers due to rounding.
Notes:
a. EPA, Inventory of U.S. Greenhouse Gas Emissions and Sinks, 1990-2016, Tables ES-2 and 3-5, April 2018.
b. Number of wells from EIA, The Distribution of U.S. Oil and Natural Gas Wells by Production Rate, 2017 (data from 2016). A smaller number of entities operate these wells. According to EIA, the number of well operators is approximately 15,000 (personal correspondence, May 15, 2018).
c. EIA, "Petroleum and Other Liquids, Company Level Imports" (data from February 2018). This group of companies does not include those that import "asphalt road oil," "lubricants," "wax," or "petrochemical feedstocks," which would not be subject to the above tax framework.
d. Based on the number of "operating" refineries. EIA, "Number and Capacity of Petroleum Refineries," data from 2017. Some of these refineries may produce only lubricating oils and asphalt.
e. EPA, Inventory of U.S. Greenhouse Gas Emissions and Sinks, 1990-2016. This figure includes underground and surface mines.
f. Eight companies supplied imported coal to power plants in December 2017. Ten power plants used imported coal in December 2017 (EIA Form EIA-923, https://www.eia.gov/electricity/data/eia923/). In recent years, imported coal use has decreased: In 2006, the United States imported approximately 36 million tons of coal, decreasing to about 8 million tons by 2017 (EIA, Quarterly Coal Report, Table 4).
g. Coal Option 2 is less comprehensive than Coal Option 1, because it would not attach a carbon price to the coal that is used by entities other than electric utilities. In 2016, 95% of coal emissions were from electric utilities. The industrial sector accounted for the vast majority of the remainder. (See EPA, Inventory of U.S. Greenhouse Gas Emissions and Sinks, 1990-2016, Table 3-5.) Policymakers may consider a direct emissions approach (i.e., "downstream") for coal-fired electric utilities, because they already continuously monitor their CO2 emissions and report electronically to the EPA: Section 821 of the 1990 Clean Air Act Amendments requires electric generating facilities affected by the acid rain provisions of Title IV to monitor CO2 emissions. In addition, some argue that this approach would provide a greater stimulus to develop CCS technology. Although a price signal would be sent in either case—thus (in theory) encouraging CCS development—some contend that if coal is taxed upstream at the extraction point, some of the price signal may be weakened before it reaches coal-fired emission sources. For more information on CCS technology, see CRS Report R42532, Carbon Capture and Sequestration (CCS): A Primer, by Peter Folger.
h. EIA, Electric Power Annual, Table 4.1 (data from 2016).
i. Number of wells from EIA, The Distribution of U.S. Oil and Natural Gas Wells by Production Rate, 2017 (data from 2016).
j. EIA data indicate that 28 natural gas pipelines imported oil in 2017 ("U.S. Natural Gas Imports by Point of Entry"). In addition, there are 11 liquefied natural gas import terminals (California Energy Commission, http://www.energy.ca.gov/lng/worldwide_united_states.html).
k. CRS used 2016 data for this estimate, because 2017 data were not available for all of the data points. Although Natural Gas Option 2 would apply to fewer entities than would Natural Gas Option 1, Option 2 would cover a smaller percentage of emissions from natural gas combustion. A substantial portion of natural gas that is produced domestically does not pass through a natural gas processing facility before it reaches an end user, including exported natural gas. In 2016, this unprocessed volume was approximately 8.2 trillion cubic feet (tcf), accounting for 29% of natural gas "marketed production." CRS calculated this figure using EIA "marketed production" (28.5 tcf) and "natural gas processed" (20.3 tcf) data.
To estimate the percentage of total GHG emissions covered under Option 2, CRS assumed that all of the natural gas exports (2.3 tcf in 2016) were processed, yielding 18.0 tcf processed for U.S. consumption. Combined with imported natural gas (3.0 tcf in 2016), the aggregate volume (21.0 tcf) accounts for 77% of natural gas consumption in 2016 (27.1 tcf). This equates to approximately 17% of total U.S. GHG emissions. In addition, under Option 2, policymakers could cover some portion of the CH4 emissions from "natural gas systems." This could increase the total GHG emission coverage by a range of 0.4% (processing and distribution) to 1.5% (processing, distribution, and all transmission/storage), thus yielding the 17%-19% range in the table.
l. EIA, "Natural Gas Annual Respondent Query System, Processing Capacity" (data for 2014).
m. EIA requires certain entities to submit specific natural gas data on Form EIA-176. In 2016, 1,679 entities reported natural gas deliveries (25.5 tcf in aggregate) to end users: electricity generators, industry, commercial and residential consumers. The end-use data include domestic and imported natural gas. This accounts for 94% of natural gas consumption. In addition, policymakers could attach a tax to natural gas liquids at fractionators that remove natural gas liquids from natural gas. In 2016, approximately 1.6 tcf of natural gas liquids were extracted (calculated by subtracting "dry production" from "marketed production"). Combining Form EIA-176 entities with natural gas liquid fractionators would apply a carbon price to approximately 100% of natural gas consumption, covering 23% of GHG emissions. In addition, the Form 176 entities report data that would address some portion of the emissions associated with "CH4 from natural gas systems," such as onsite use and fugitive emissions. It is uncertain what portion would be covered by the reporting entities. In this estimate CRS assumes that all of the CH4 from natural gas systems, excepting the portion attributed to production, would be addressed by applying a tax to these entities. This would add 0.9% to the coverage, thus attaching a price to approximately 24% of total GHG emissions.
n. Natural gas liquid fractionators report information to EPA pursuant to its GHG reporting program. In 2016, EPA identified 123 natural gas fractionators that reported GHG information to EPA (https://www.epa.gov/ghgreporting/ghgrp-suppliers-natural-gas-and-natural-gas-liquids).
o. Although there are no upstream transaction points that offer an opportunity to attach a price to all of these emissions, policymakers could potentially address a considerable portion by attaching a tax to the sale of synthetic fertilizers. EPA estimates that N2O emissions from the use of synthetic fertilizers account for approximately 23% of this emission source—1.0% of total U.S. GHG emissions (EPA, Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990-2016, Table 5-17, 2018). A tax on synthetic fertilizers may lead to less use, but it could "lead to other practices that release nitrogen" (Gilbert Metcalf and David Weisbach, "The Design of a Carbon Tax," Harvard Environmental Law Review, vol. 33, no. 2 [2009]). In its mandatory reporting program, EPA considered requiring ammonia manufacturers and nitric acid producers to report on their synthetic fertilizer production. The agency ultimately decided to eliminate this requirement, because, according to EPA, it would not address the more than 50% of synthetic fertilizer that is imported or produced in other industries (75 Federal Register 48744, August 11, 2010).
p. USDA, Farms and Land in Farms, 2017 Summary, 2018.
q. Number of pipeline systems from EIA, "About U.S. Natural Gas Pipelines" (based on 2007-2008 data), https://www.eia.gov/naturalgas/archive/analysis_publications/ngpipeline/index.html.
r. In 2016, 371 natural gas LDCs reported CO2 emissions pursuant to EPA's GHG reporting program: https://www.epa.gov/ghgreporting/ghgrp-suppliers-natural-gas-and-natural-gas-liquids.
s. Cattle farm total from USDA, 2012 Census, Table 1, https://agcensus.usda.gov/Publications/.
t. The 1987 Montreal Protocol, implemented in the United States by the 1990 Clean Air Act Amendments, is phasing out ozone-depleting substances, such as chlorofluorocarbons. This development led to increased production of some substitutes, such as hydrofluorocarbons (HFCs) and perfluorocarbons, which are extremely potent GHGs. For example, HFC-134a, which accounts for the largest percentage of HFC emissions, has a global warming potential of 1,430 (see footnote 20). These materials are used in a wide variety of commercial and residential equipment, including refrigeration and air conditioning units. According to EPA, motor vehicle air conditioning units account for the largest HFC emission source. HFC emissions enter the atmosphere during "equipment manufacture and operation (as a result of component failure, leaks, and purges), as well as at servicing and disposal events" (EPA, Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990-2016). The United States and other nations agreed to phase down HFCs under the Kigali Amendment to the Montreal Protocol. The United States has not ratified the Kigali Amendment to date, but enough countries have ratified to enable the treaty to enter into force. EPA has regulated some uses of HFC under the Clean Air Act, but certain limits have been struck down in litigation. For more information, see EPA's website, https://www.epa.gov/ozone-layer-protection/recent-international-developments-under-montreal-protocol. See also CRS In Focus IF10904, Potential Hydrofluorocarbon Phase Down: Issues for Congress, by Jane A. Leggett, and CRS Legal Sidebar LSB10154, D.C. Circuit Rejects EPA's Efforts to Ban Hydrofluorocarbons: Part 1, by Linda Tsang.
u. Under EPA's GHG reporting program, 14 facilities reported as fluorinated gas producers in 2016. This includes facilities that produce HFCs, perfluorocarbons, sulfur hexafluoride, nitrogen trifluoride, fluorinated ethers, and chlorofluorocarbons and hydrochlorofluorocarbons, including chlorodifluoromethane. (See https://www.epa.gov/ghgreporting/ghgrp-chemicals.) The number of gas importers comes from an investigation and related document prepared by the International Trade Commission (Investigation No. 731-TA-1279, Hydrofluorocarbon Blends and Components from China, 2015, p. 77, https://www.usitc.gov/publications/701_731/pub4558.pdf). An upstream price on fluorinated gases would not impact HFC emissions in existing equipment. Thus the percentage of coverage would be less than the total GHG contribution (2.4%). Some observers have suggested an alternative approach to pricing HFC emissions. For example, policymakers could set up a deposit-refund system at which an initial presumptive tax/fee would be applied to the manufacture or purchase of an item (e.g., vehicle air conditioning unit) and a refund would be provided upon proof of proper disposal (Gilbert Metcalf and David Weisbach, "The Design of a Carbon Tax," Harvard Environmental Law Review, vol. 33, no. 2 [2009]). This approach would cover only HFC emissions from the equipment in the fee/rebate program.
v. Number of landfills from EPA, Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990-2016. For more information, see CRS Report R43860, Methane: An Introduction to Emission Sources and Reduction Strategies, coordinated by Richard K. Lattanzio.
w. In an upstream carbon tax system, policymakers would attach a price to fossil fuels before the fuel use. Relatively small quantities of fossil fuels are used for a wide range of nonenergy purposes, including as ingredients in plastics, asphalt, lubricants, or other products. Of the total carbon consumed for nonenergy purposes, approximately 60% is stored in the final product and not released to the atmosphere—thus the estimated 0.8% in the table. The remaining carbon is released as emissions, which may occur during the manufacturing process or during the product's use, such as solvent application (EPA, Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990-2016). Many carbon tax proposals would provide a tax credit when carbon is stored permanently in end products.
x. EPA, Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990-2016, Table 3-36.
y. Hog farm total from USDA, 2012 Census, Table 1, https://agcensus.usda.gov/Publications/.
z. EPA, Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990-2016.
aa. U.S. Geological Survey, Mineral Commodity Summaries 2018, 2018 (data for 2017), https://minerals.usgs.gov/minerals/pubs/mcs/2018/mcs2018.pdf.
bb. Number of facilities based on EPA's GHG reporting program data. See https://www.epa.gov/ghgreporting/ghgrp-minerals.
Author Contact Information
1. |
U.S. Global Change Research Group, Fourth National Climate Assessment Volume II: Impacts, Risks, and Adaptation in the United States, Chapter 1, 2018, https://nca2018.globalchange.gov. |
2. |
For more details, see Organization for Economic Cooperation and Development, Effective Carbon Rates 2018: Pricing Carbon Emissions Through Taxes and Emissions Trading, 2018, http://www.oecd.org/tax/effective-carbon-rates-2018-9789264305304-en.htm; and the Carbon Tax Center website at http://www.carbontax.org/where-carbon-is-taxed. |
3. |
A number of U.S. states have taken action requiring GHG emission reductions, including California and the Regional Greenhouse Gas Initiative (RGGI)—a coalition of nine states from the Northeast and Mid-Atlantic regions. The RGGI is a cap-and-trade system that took effect in 2009 and applies to carbon dioxide emissions from electric power plants. (See CRS Report R41836, The Regional Greenhouse Gas Initiative: Lessons Learned and Issues for Congress, by Jonathan L. Ramseur.) California established a cap-and-trade program that took effect in 2013. California's cap covers multiple GHGs, which account for approximately 85% of California's GHG emissions. For more details, see the California Air Resources Board website, https://www.arb.ca.gov/cc/capandtrade/capandtrade.htm. |
4. |
An exhaustive documentation of these varied perspectives is beyond the scope of this report. |
5. |
Speech by United Nations Secretary-General Antonio Guterres, September 10, 2018, https://www.un.org/sg/en/content/sg/statement/2018-09-10/secretary-generals-remarks-climate-change-delivered. |
6. |
See, for example, Heather Smith, "Climate Change: Even Worse That We Thought," Sierra Club Magazine, October 2018. |
7. |
Intergovernmental Panel on Climate Change (IPCC), Global Warming of 1.5˚C, 2018, http://www.ipcc.ch/report/sr15/. The IPCC is organized under the auspices of the United Nations. According to the IPCC website, "thousands of people from all over the world contribute to the work of the IPCC…. An open and transparent review by experts and governments around the world is an essential part of the IPCC process, to ensure an objective and complete assessment and to reflect a diverse range of views and expertise. Through its assessments, the IPCC identifies the strength of scientific agreement in different areas and indicates where further research is needed. The IPCC does not conduct its own research" (https://www.ipcc.ch/about/). |
8. |
Established by the Global Change Research Act of 1990 (P.L. 101-606), the U.S. Global Change Research Program coordinates and integrates federal research and applications to understand, assess, predict, and respond to human-induced and natural processes of global change. Thirteen federal agencies and departments participate in the program. |
9. |
See, for example, David Kreutzer el al., "The State of Climate Science: No Justification for Extreme Policies," Heritage Foundation, 2016, https://www.heritage.org/environment/report/the-state-climate-science-no-justification-extreme-policies; Marlo Lewis, "You Don't Have to Be a Climate Skeptic to Oppose a Carbon Tax," Competitive Enterprise Institute, 2018, https://cei.org/blog/you-dont-have-be-climate-skeptic-oppose-carbon-tax. |
10. |
See, for example, letter from 20 organizations to Paul Ryan (then-Speaker of the House) and Kevin McCarthy (then-Majority Leader), July 9, 2018, https://www.americanenergyalliance.org/wp-content/uploads/2018/07/CarbonTaxLetterUpdated.pdf; and Oren Cass, "The Carbon-Tax Shell Game," National Affairs, 2015. |
11. |
However, this procedural point would likely be the subject of debate: A ruling on whether a policy instrument is a user fee or a tax measure may depend on the nature of the charge rather than its label. This issue is beyond the scope of this report. |
12. |
As expressed in CO2-equivalents. See U.S. Environmental Protection Agency, Inventory of U.S. Greenhouse Gas Emissions and Sinks, 1990-2016, April 2018. |
13. |
This differs from a price system that applies to energy content, such a tax based on British thermal units (Btu). In 1993, President Clinton proposed a deficit reduction package that included a tax based on energy content, measured in Btu. The goals of the proposal were to promote energy conservation and raise revenue. At the time, the proposed tax would have generated a new revenue stream of about $30 billion per year. The proposal was met with strong opposition and was not enacted. Congress ultimately enacted an approximately 5-cent per gallon increase in the motor fuels taxes. |
14. |
Carbon intensity refers to the amount of CO2 emissions generated per unit of energy. The CO2 emission intensity of coal is approximately 30% more than oil and approximately 80% more than natural gas. |
15. |
For more details, see CRS Report R45472, Market-Based Greenhouse Gas Emission Reduction Legislation: 108th Through 115th Congresses, by Jonathan L. Ramseur. Other legislation may indirectly reduce GHG emissions, for example, by providing tax or other incentives for renewable energy or CCS activities. |
16. |
For more details, see the council's website at https://www.clcouncil.org/. |
17. |
For more information, see CRS In Focus IF10589, FY2019 Funding for CCS and Other DOE Fossil Energy R&D, by Peter Folger. |
18. |
The House passed an identical resolution in the 114th Congress (H.Con.Res. 89). |
19. |
See, for example, H.R. 2042 in the 108th Congress, S. 3639 in the 109th Congress, and S. 309 in the 110th Congress. |
20. |
GWP is an index developed by the IPCC that allows comparisons of the heat-trapping ability of different gases over a period of time, typically 100 years. Consistent with international GHG reporting requirements, EPA's most recent GHG inventory (2018) uses the GWP values presented in the IPCC's 2007 Fourth Assessment Report. For example, based on these GWP values, a metric ton of methane equates to 25 metric tons of CO2 when averaged over a 100-year time frame. The IPCC has since updated the 100-year GWP estimates, with some increasing and some decreasing. For example, the IPCC 2013 Fifth Assessment Report reported the 100-year GWP for methane as ranging from 28 to 36. The uncertainty in the GWP for a particular GHG could be of interest for policymakers. See Donald Marron et al., Taxing Carbon: What, Why, and How, Tax Policy Center, 2015, p. 4. |
21. |
40 C.F.R. Part 75. |
22. |
The FY2008 Consolidated Appropriations Act (P.L. 110-161) directed EPA to establish a mandatory reporting program for "appropriate thresholds in all sectors of the economy." EPA established its Greenhouse Gas Reporting Program in 2009, which is codified in 40 C.F.R. Part 98. For more information, see http://www.epa.gov/ghgreporting. |
23. |
EPA's GHG reporting regulations also apply to suppliers of fossil fuels, which include nearly 1,000 fossil-fuel-reporting suppliers. |
24. |
A natural gas fractionator separates natural gas liquids (ethane, propane, butane) from the natural gas stream. |
25. |
See CRS In Focus IF10823, The Oil Spill Liability Trust Fund Tax: Reauthorization Issues and Legislation in the 115th Congress, by Jonathan L. Ramseur. |
26. |
See CRS Report R45261, The Black Lung Program, the Black Lung Disability Trust Fund, and the Excise Tax on Coal: Background and Policy Options, by Scott D. Szymendera and Molly F. Sherlock. |
27. |
For a description of the current U.S. commitment, see CRS In Focus IF10239, President Obama Pledges Greenhouse Gas Reduction Targets as Contribution to 2015 Global Climate Change Deal, by Jane A. Leggett. President Trump announced an intention to withdraw the United States from the agreement when eligible in 2020. No action has been taken to withdraw or modify the U.S. pledged GHG reduction contribution. See CRS In Focus IF10668, Potential Implications of U.S. Withdrawal from the Paris Agreement on Climate Change, by Jane A. Leggett. |
28. |
Yunguang Chen and Marc Hafstead, "Using a Carbon Tax to Meet U.S. International Climate Pledges," Climate Change Economics, 2018. The modeled carbon tax system applied to emissions from fossil fuel combustion. |
29. |
For example, multiple parties prepared estimates during the development of H.R. 2454 (which passed the House on June 26, 2009) in the 111th Congress. That proposal intended to reduce GHG emissions to 17% below 2005 levels by 2020. The emission allowance price estimates needed to meet emission targets ranged from $16/mtCO2e to $49/mtCO2e in 2015, with the estimated range increasing over time. |
30. |
By "marginal," economists mean an additional, small increment—in other words, the benefits associated with making an additional, small amount of emissions reduction, not the total emissions reductions from a policy. |
31. |
See, for example, Organisation for Economic Co-operation and Development, "The Social Cost of Carbon," in Cost-Benefit Analysis and the Environment: Further Developments and Policy Use, 2018. |
32. |
Net benefits refers to the beneficial value of abating GHG emissions (e.g., avoiding heat stress deaths) minus the positive impacts that climate change could bring (e.g., increased agricultural productivity in some regions). One challenge in these metrics is that the damages and the benefits of climate change often impact different groups and sometimes at different times. In addition, the calculation of costs and benefits can vary based on the geographic scope considered. See CRS Report R45119, EPA's Proposal to Repeal the Clean Power Plan: Benefits and Costs, by Kate C. Shouse. |
33. |
For more information, see CRS In Focus IF10625, Social Costs of Carbon/Greenhouse Gases: Issues for Congress, by Jane A. Leggett. |
34. |
The SC-CO2 measures the net benefits of relatively small (marginal) reductions in CO2 emissions. The federal SC-CO2 values used in rulemakings have been based on business-as-usual projections, which may not reflect the economically efficient GHG emission levels in the long-term. See for example, International Monetary Fund, Fiscal Policy to Mitigate Climate Change: A Guide for Policymakers (Washington, DC: International Monetary Fund, 2012), https://www.imf.org/en/Publications/Books/Issues/2016/12/31/Fiscal-Policy-to-Mitigate-Climate-Change-A-Guide-for-Policymakers-25864. |
35. |
See public comments on the SC-CO2 for certain regulatory uses contained in the docket for Office of Management and Budget, Technical Support Documents: Update of the Social Cost of Carbon for Regulatory Impact Analysis under Executive Order No. 12866, 2014, https://www.regulations.gov/document?D=OMB-2013-0007-0063. See also Richard S. J. Tol, "Is the Uncertainty About Climate Change Too Large for Expected Cost-Benefit Analysis?," Climatic Change, 2003. |
36. |
See the section "Considerations for the Scope—Domestic or Global—of the SCC [i.e., SC-CO2]" in CRS Report R45119, EPA's Proposal to Repeal the Clean Power Plan: Benefits and Costs, by Kate C. Shouse. |
37. |
See CRS Report R44657, Federal Citations to the Social Cost of Greenhouse Gases, by Jane A. Leggett. |
38. |
Policy analysts have been exploring options to mitigate some of the problems in applying this approach to climate change. See, for example, Francis Dennig, "Climate Change and the Re-Evaluation of Cost-Benefit Analysis," Climatic Change, 2017. |
39. |
See, for example, M. Granger Morgan et al. "Why Conventional Tools for Policy Analysis Are Often Inadequate for Problems of Global Change," Climatic Change, vol. 41 (1999), pp. 271-281; Robert S. Pindyck, "Uncertainty in Environmental Economics," in Review of Environmental Economics and Policy (Oxford: Oxford University Press, 2007). |
40. |
Examples of tipping points include "the destabilization of the West Antarctic ice sheet or rapid methane release from thawing permafrost." See the U.S. Global Change Research Program, Fourth National Climate Assessment, Volume II: Impacts, Risks, and Adaptation in the United States, 2018. |
41. |
See, for example, IPCC, Global Warming of 1.5˚C, Chapter 3, http://www.ipcc.ch/report/sr15/. |
42. |
Not all businesses within a sector may be affected similarly. For example, under a carbon tax system, an aluminum company using electricity produced with hydropower would experience less cost increase than a company using electricity produced with coal. In addition, some businesses may be more energy efficient than others or use less emitting processes. Some may be able to reduce their emissions in response to a carbon tax at lower cost than others. |
43. |
See CRS Report R45472, Market-Based Greenhouse Gas Emission Reduction Legislation: 108th Through 115th Congresses, by Jonathan L. Ramseur. |
44. |
See, for example, Adele Morris, Making Border Carbon Adjustments Work in Law and Practice, Tax Policy Center, 2018. |
45. |
See, for example, Marco Sakai and John Barrett, "Border Carbon Adjustments: Addressing Emissions Embodied in Trade," Energy Policy, 2016; Sam Kortum and David Weisbach, "Border Adjustment for Carbon Emissions," Resources for the Future, 2016; Carolyn Fischer et al., "Carbon Taxes and Energy-Intensive Trade-Exposed Industries," in Implementing a U.S. Carbon Tax: Challenges and Debates, ed. Ian Parry et al. (Washington, DC: International Monetary Fund, 2015). |
46. |
Congressional Budget Office, Border Adjustments for Economywide Policies That Impose a Price on Greenhouse Gas Emissions, 2013. |
47. |
See, for example, Joel Trachtman, "WTO Law Constraints on Border Tax Adjustment and Tax Credit Mechanisms to Reduce the Competitive Effects of Carbon Taxes," Resources for the Future, 2016. |
48. |
See, for example, Warwick McKibbin et al., "The Role of Border Carbon Adjustments in a U.S. Carbon Tax," Climate Change Economics, vol. 9, no. 1 (2018). |
49. |
CRS Report R44609, Climate Change: Frequently Asked Questions About the 2015 Paris Agreement, by Jane A. Leggett and Richard K. Lattanzio. |
50. |
EPA, Office of Air and Radiation, Tools of the Trade: A Guide to Designing and Operating a Cap and Trade Program for Pollution Control, 2003, Glossary. |
51. |
See, for example, McKibbin et al., "The Role of Border Carbon Adjustments in a U.S. Carbon Tax"; Morris, Making Border Carbon Adjustments Work in Law and Practice, 2018; Joseph Aldy, "Frameworks for Evaluating Policy Approaches to Address the Competitiveness Concerns of Mitigating Greenhouse Gas Emissions," National Tax Journal, 2017. |
52. |
In economic literature, this measure is referred to as the tax incidence. |
53. |
See, for example, Jared C. Carbone et al., Deficit Reduction and Carbon Taxes: Budgetary, Economic, and Distributional Impacts, Resources for the Future, 2013; Adele Morris and Aparna Mathur, "A Carbon Tax in Broader U.S. Fiscal Reform: Design and Distributional Issues," Center for Climate and Energy Solutions, 2014. |
54. |
See CRS Report R45472, Market-Based Greenhouse Gas Emission Reduction Legislation: 108th Through 115th Congresses, by Jonathan L. Ramseur. |
55. |
See CRS Report R45145, Overview of the Federal Tax System in 2018, by Molly F. Sherlock and Donald J. Marples. |
56. |
See, for example, Lawrence Goulder et al., Impacts of a Carbon Tax Across US Household Income Groups: What are the Equity-Efficiency Trade-Offs?, Resources for the Future, 2018; John W. Diamond and George R. Zodrow, The Effects of Carbon Tax Policies on the Economy and the Welfare of Households, Columbia University, SIPA Center on Global Energy Policy, 2018; Joseph Rosenberg, Distributional Implications of a Carbon Tax, SIPA Center on Global Energy Policy, 2018; Chen and Hafstead, "Using a Carbon Tax to Meet U.S. International Climate Pledges." |
57. |
In the context of EPA's Clean Power Plan rulemaking and more recently proposed Affordable Clean Energy substitute rule, whether to include co-benefits in calculated net benefits has generated controversy. See CRS Report R44341, EPA's Clean Power Plan for Existing Power Plants: Frequently Asked Questions, by James E. McCarthy et al.; and CRS Report R45119, EPA's Proposal to Repeal the Clean Power Plan: Benefits and Costs, by Kate C. Shouse. |
58. |
EPA, Climate Change in the United States: Benefits of Global Action, 2015, https://www.epa.gov/cira. See also GAO, Information on Potential Economic Effects Could Help Guide Federal Efforts to Reduce Fiscal Exposure, 2017, https://www.gao.gov/assets/690/687466.pdf. |
59. |
See, for example, the House-passed resolution "expressing the sense of Congress that a carbon tax would be detrimental to the United States economy" (July 19, 2018, H.Con.Res. 119); and letter from House Speaker Paul Ryan and Majority Leader Kevin McCarthy from American Energy Alliance et al., July 9, 2018, https://www.americanenergyalliance.org/wp-content/uploads/2018/07/CarbonTaxLetterUpdated.pdf. |
60. |
Economic welfare may be defined as "a notion of household well-being encompassing everything that individuals value—market goods and services measured by GDP plus nonmarket items (e.g., children at home, leisure time)." Glossary in Parry et al., Implementing a U.S. Carbon Tax. |
61. |
Robertson Williams and Casey J. Wichman, "Macroeconomic Effects of Carbon Taxes," in Implementing a U.S. Carbon Tax: Challenges and Debates, ed. Ian Parry et al., 2015. |
62. |
See, for example, Diamond and Zodrow, The Effects of Carbon Tax Policies on the U.S. Economy and the Welfare of Households; Jared C. Carbone et al., Deficit Reduction and Carbon Taxes; Ian Parry and Robertson C. Williams III, Moving U.S. Climate Policy Forward: Are Carbon Taxes the Only Good Alternative?, Resources for the Future, 2011; Warwick McKibben et al., The Potential Role of a Carbon Tax in U.S. Fiscal Reform, Brookings Institution, 2012. |
63. |
For further information, see Dale W. Jorgenson et al., Double Dividend: Environmental Taxes and Fiscal Reform in the United States (Cambridge, MA: MIT Press, 2013); and Jaume Freire-González, "Environmental Taxation and the Double Dividend Hypothesis in CGE Modelling Literature: A Critical Review," Journal of Policy Modeling, 2018. |
64. |
See Goulder et al., Impacts of a Carbon Tax across US Household Income Groups; Chen and Hafstead, "Using a Carbon Tax to Meet U.S. International Climate Pledges"; Williams and Wichman, "Macroeconomic Effects of Carbon Taxes"; Sugandha D. Tuladhar et al., "Environmental Policy for Fiscal Reform: Can a Carbon Tax Play a Role?," National Tax Journal, 2015; Sebastian Rausch and John Reilly, "Carbon Taxes, Deficits, and Energy Policy Interactions," National Tax Journal, 2015; NERA Economic Consulting (prepared for National Association of Manufacturers), Economic Outcomes of a U.S. Carbon Tax, 2013; Parry and Williams, Moving U.S. Climate Policy Forward. |
65. |
See Diamond and Zodrow, The Effects of Carbon Tax Policies on the U.S. Economy and the Welfare of Households; James R. McFarland et al., "Overview of the EMF 32 Study on U.S. Carbon Tax Scenarios," Climate Change Economics, 2018; Dale Jorgenson et al., "Carbon Taxes and Fiscal Reform in the United States," National Tax Journal, 2015; Carbone et al., Deficit Reduction and Carbon Taxes; Parry and Williams, Moving U.S. Climate Policy Forward; McKibben et al., The Potential Role of a Carbon Tax in U.S. Fiscal Reform. |
66. |
See Diamond and Zodrow, The Effects of Carbon Tax Policies on the U.S. Economy and the Welfare of Households, 2018. |
67. |
In addition, several economic studies prepared before the enactment of the TCJA found that when carbon tax revenues were used to reduce marginal tax rates on capital income—which includes corporate income tax and personal income tax on interest, dividends, and capital gains—the economy-wide impacts were positive relative to the baseline. See McFarland et al., "Overview of the EMF 32 Study on U.S. Carbon Tax Scenarios"; Dale Jorgenson et al., "The Welfare Consequences of Taxing Carbon," Climate Change Economics, 2018; Jorgenson et al., "Carbon Taxes and Fiscal Reform in the United States"; Carbone et al., Deficit Reduction and Carbon Taxes; McKibben et al., The Potential Role of a Carbon Tax in U.S. Fiscal Reform. |
68. |
See McFarland et al., "Overview of the EMF 32 Study on U.S. Carbon Tax Scenarios"; Capital Alpha Partners, The Carbon Tax: Analysis of Six Potential Scenarios, 2018 (although both of these analyses were published in 2018, they were prepared before the enactment of the TCJA); Jorgenson et al., "Carbon Taxes and Fiscal Reform in the United States"; Carbone et al., Deficit Reduction and Carbon Taxes; Parry and Williams, Moving U.S. Climate Policy Forward; McKibben et al., The Potential Role of a Carbon Tax in U.S. Fiscal Reform. |
69. |
The carbon tax framework is discussed in further detail in the study's companion publication: John Larsen et al., Energy and Environmental Implications of a Carbon Tax in the United States, SIPA Center on Global Energy Policy, 2018. |
70. |
See, for example, National Association of Manufacturers, Economic Outcomes of a U.S. Carbon Tax, 2013, Executive Summary. |
71. |
See Aparna Mathur and Adele Morris, "Distributional Effects of a Carbon Tax in Broadest U.S. Fiscal Reform," Energy Policy, 2014. |
72. |
Terry Dinan, Offsetting a Carbon Tax's Costs on Low-Income Households, Congressional Budget Office, 2012. |
73. |
Mathur and Morris state that "a number of large-scale general equilibrium models (CGE models) suggest that in the short to medium run, the burden of a carbon tax will be mostly passed forward into higher consumer prices." Mathur and Morris, "Distributional Effects of a Carbon Tax in Broadest U.S. Fiscal Reform." See Williams and Wichman, "Macroeconomic Effects of Carbon Taxes"; Terry Dinan, "Offsetting a Carbon Tax's Burden on Low-Income Households," Table 7.1, in Implementing a U.S. Carbon Tax. |
74. |
Adele Morris and Aparna Mathur, "The Distributional Burden of a Carbon Tax," in Implementing a U.S. Carbon Tax. |
75. |
See John Horowitz et al., Office of Tax Analysis, Methodology for Analyzing a Carbon Tax, 2017. |
76. |
Justin Caron et al., "Distributional Implications of a National CO2 Tax in the U.S. Across Income Classes and Regions: A Multi-Model Overview," Climate Change Economics, 2018. |
77. |
See Rosenberg, Distributional Implications of a Carbon Tax; Goulder et al., Impacts of a Carbon Tax across US Household Income Groups; Rausch and Reilly, "Carbon Taxes, Deficits, and Energy Policy Interactions"; Marron et al., Taxing Carbon: What, Why, and How; Robertson Williams et al., "The Initial Incidence of a Carbon Tax Across Income Groups," National Tax Journal, 2015; Jorgenson et al., "Carbon Taxes and Fiscal Reform in the United States"; Mathur and Morris, "Distributional Effects of a Carbon Tax in Broadest U.S. Fiscal Reform." |
78. |
A comparison of these differences is beyond the scope of this report. |
79. |
Rosenberg, Distributional Implications of a Carbon Tax. |
80. |
See Caron et al., "Distributional Implications of a National CO2 Tax in the U.S. Across Income Classes and Regions"; John Horowitz et al., Office of Tax Analysis, Methodology for Analyzing a Carbon Tax, 2017 (this study also includes a scenario splitting the revenue three ways among lump-sum, labor tax rate reduction, and corporate tax rate reduction); Jorgenson et al., "The Welfare Consequences of Taxing Carbon"; Rausch and Reilly, "Carbon Taxes, Deficits, and Energy Policy Interactions." |
81. |
Caron et al., "Distributional Implications of a National CO2 Tax in the U.S. across Income Classes and Regions." |
82. |
As one point of reference, under H.R. 2454 (111th Congress) such industries would have received approximately 15% of the emission allowance value—analogous to 15% of carbon tax revenue—through 2025, steadily decreasing to zero thereafter. |
83. |
Fischer et al., "Carbon Taxes and Energy-Intensive Trade-Exposed Industries"; see also Liwayway Adkins et al., Carbon Pricing with Output-Based Subsidies: Impacts on U.S. Industries over Multiple Time Frames, National Center for Environmental Economics, 2012. |
84. |
Government of Canada, "Putting a Price on Pollution: How It Will Work," https://www.canada.ca/en/services/environment/weather/climatechange/climate-action/pricing-carbon-pollution.html. |
85. |
Fischer et al., "Carbon Taxes and Energy-Intensive Trade-Exposed Industries." |
86. |
See Larsen et al., Energy and Environmental Implications of a Carbon Tax in the United States. |
87. |
See Adele Morris, Build a Better Future for Coal Workers and Their Communities, Brookings Institution, 2016. |
88. |
See CRS Report R45472, Market-Based Greenhouse Gas Emission Reduction Legislation: 108th Through 115th Congresses, by Jonathan L. Ramseur. |
89. |
See CRS Report R42532, Carbon Capture and Sequestration (CCS): A Primer, by Peter Folger. |
90. |
In general, biological sequestration efforts are more challenging to quantify than emission reductions from other sources, such as power plants. |
91. |
For more details, see Table 1 in CRS Report R41836, The Regional Greenhouse Gas Initiative: Lessons Learned and Issues for Congress, by Jonathan L. Ramseur. |
92. |
For more information, see California's Legislative Analyst's Office, The 2017-18 Budget: Cap-and-Trade, 2017. |
93. |
For a comparison of reduction estimates from several studies, see Table 1 in Morris and Mathur, "A Carbon Tax in Broader U.S. Fiscal Reform." |
94. |
The EMF 32 study led to multiple papers published in a special issue in Climate Change Economics (March 2018). See Allen A. Fawcett et al., "Introduction to the EMF 32 Study on U.S. Carbon Tax Scenarios," Climate Change Economics, vol. 9, no. 1 (2018). These papers are available at https://www.worldscientific.com/toc/cce/09/01. |
95. |
James R. McFarland et al., "Overview of the EMF 32 Study on U.S. Carbon Tax Scenarios," Climate Change Economics, vol. 9, no. 1 (2018). |
96. |
For a description of the current U.S. commitment, see CRS In Focus IF10239, President Obama Pledges Greenhouse Gas Reduction Targets as Contribution to 2015 Global Climate Change Deal, by Jane A. Leggett. Although President Trump announced an intention to withdraw the United States from the agreement when eligible in 2020, no action has been taken to withdraw or modify the U.S. pledged GHG reduction contribution. See CRS In Focus IF10668, Potential Implications of U.S. Withdrawal from the Paris Agreement on Climate Change, by Jane A. Leggett. |
97. |
Starting in 2010, EPA regulations have required large emission sources and fuel suppliers (among others) to annually report GHG emissions to EPA. See EPA, "Learn About the Greenhouse Gas Reporting Program (GHGRP)," https://www.epa.gov/ghgreporting/learn-about-greenhouse-gas-reporting-program-ghgrp. |
98. |
See Marc Hafstead et al., "Adding Quantity Certainty to a Carbon Tax Through a Tax Adjustment Mechanism for Policy Pre-Commitment," Harvard Environmental Law Review, 2017; Brian Murray et al., "Increasing Emissions Certainty Under a Carbon Tax," Harvard Environmental Law Review, 2017; and Dieter Helm et al., "Credible Carbon Policy," in Climate Change Policy, ed. Dieter Helm, 2005. |
99. |
See William Pizer, Prices vs. Quantities Revisited: The Case of Climate Change, Resources for the Future, 1997. |
100. |
Historically, the electric power sector accounted for the largest percentage, but emissions in this sector have declined considerably in recent years. Between 2006 and 2016, electric power emissions decreased by 23%. EPA, Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990–2016, April 2018, https://www.epa.gov/ghgemissions/inventory-us-greenhouse-gas-emissions-and-sinks. |
101. |
See Larsen et al., Energy and Environmental Implications of a Carbon Tax in the United States; McFarland et al., "Overview of the EMF 32 Study on U.S. Carbon Tax Scenarios." |
102. |
For a further discussion see Larsen et al., Energy and Environmental Implications of a Carbon Tax in the United States. |
103. |
For further information on these issues, see CRS In Focus IF10871, Vehicle Fuel Economy and Greenhouse Gas Standards, by Richard K. Lattanzio, Linda Tsang, and Bill Canis. |
104. |
Modelers in this study analyzed four carbon tax scenarios starting in 2020: a $25/metric ton and $50/metric ton carbon tax, both increasing annually by 1% and 5%. |
105. |
One model projected revenue declines under one of the carbon price scenarios. This model also projected a much greater utilization of CCS technology than other models. See Figure 9 in McFarland et al., "Overview of the EMF 32 Study on U.S. Carbon Tax Scenarios." |
106. |
See Figure 10 in McFarland et al., "Overview of the EMF 32 Study on U.S. Carbon Tax Scenarios." |
107. |
Alexander R. Barron et al., "Policy Insights from the EMF 32 Study on U.S. Carbon Tax Scenarios," Climate Change Economics, vol. 9, no. 1, 2018. |
108. |
See Figure S4 in the supplemental materials for Barron et al., "Policy Insights from the EMF 32 Study on U.S. Carbon Tax Scenarios." |
109. |
CBO, "Options for Reducing the Deficit: 2019-2028," 2018, https://www.cbo.gov/system/files?file=2018-12/54667-budgetoptions.pdf. |
110. |
An alternative breakdown of this category could include CO2 emissions by sector: electricity, transportation, industrial, residential, and commercial. |