Regulation of greenhouse gases under the Clean Air Act
|Parts of this article (those related to two June 2014 Supreme Court decisions) are outdated. (November 2014)|
The United States Environmental Protection Agency (EPA) began regulating greenhouse gases (GHGs) under the Clean Air Act (“CAA” or “Act”) from mobile and stationary sources of air pollution for the first time on January 2, 2011. Standards for mobile sources have been established pursuant to Section 202 of the CAA, and GHGs from stationary sources are currently controlled under the authority of Part C of Title I of the Act. The basis for regulations were upheld in the United States Court of Appeals for the District of Columbia in June 2012.
- 1 Historical Context
- 2 Timeline
- 3 Contributors to, and the Consequences of, Climate Change
- 4 Regulatory Approaches Under the Clean Air Act for Reducing Greenhouse Gas Emissions
- 5 The Suitability of the Clean Air Act for Regulating Greenhouse Gases
- 6 The Influence of Stakeholders in Shaping How Greenhouse Gases Are Regulated Under the Clean Air Act
- 7 See also
- 8 References
Section 202(a)(1) of the CAA requires the Administrator of the EPA to establish standards, “applicable to the emission of any air pollutant from…new motor vehicles or new motor vehicle engines, which in [her] judgment cause, or contribute to, air pollution which may reasonably be anticipated to endanger public health or welfare” (emphasis added). On October 20, 1999 the International Center for Technology Assessment (ICTA) and several other parties (Petitioners) petitioned the EPA to regulate greenhouse gases from new motor vehicles under this section of the Act and thereby reduce the effects of global warming. The Petitioners argued that carbon dioxide (CO2), methane (CH4), nitrous oxide (N2O), and hydrofluorocarbons meet the definition of an air pollutant under section 302(g) of the Act, and that statements made by the EPA, other federal agencies, and the United Nations Intergovernmental Panel on Climate Change (IPCC) amounted to a finding that these pollutants are reasonably anticipated to endanger public health and welfare. Based on these factors, the Petitioners asserted that EPA had a mandatory duty to regulate greenhouse gases under section 202 of the Act and they asked the Agency to carry out that duty. On September 8, 2003, EPA denied the ICTA petition, stating that it did not have authority under the CAA to promulgate regulations to address global climate change and that CO2 and other GHGs therefore could not be considered ‘‘air pollutants’’ under the provisions of the CAA, including section 202. The Agency further stated that even if it had the authority to regulate GHGs from motor vehicles it would decline to do so as a matter of policy. The Agency maintained that regulating motor vehicle GHG emissions would neither be effective at addressing the global problem nor consistent with President Bush’s policies for addressing climate change, which centered on non-regulatory efforts such as voluntary reductions in GHGs, public-private partnerships aimed at reducing the economy’s reliance on fossil fuels, and research to address scientific uncertainties regarding climate change. The Agency’s action on the ICTA petition set the stage for a prolonged legal battle, which was eventually argued before the Supreme Court on November 29, 2006. In a 5-4 decision in Massachusetts v. Environmental Protection Agency, the Supreme Court held that “greenhouse gases fit well within the Act’s capacious definition of ‘air pollutant’ ” and that EPA therefore has statutory authority to regulate GHG emissions from new motor vehicles. The Court further ruled that “policy judgments have nothing to do with whether greenhouse gas emissions contribute to climate change and do not amount to a reasoned justification for declining to form a scientific judgment.” In EPA’s view, this required the Agency to make a positive or negative endangerment finding under Section 202(a) of the CAA.
|Date||Action Taken||Relevant Literature|
|April 2007||The U.S. Supreme Court ruled in Massachusetts v. EPA that GHGs are air pollutants covered by the Clean Air Act. The EPA may regulate GHGs if they are determined to be a danger to human health.||Supreme Court Case|
|May 2007||President George W. Bush orders EPA to use its authority under the Clean Air Act to regulate GHGs from mobile sources, working in coordination with several other federal agencies.||Executive Order 13432|
|December 2009||EPA issued its “Endangerment Finding,” which found that current and projected levels of six GHGs threaten the health and human welfare of current and future generations.||EPA Endangerment Finding|
|May 2010||EPA issued its “Tailoring Rule,” which limited air permitting guidelines to the largest stationary sources of GHGs, excluding smaller factories, restaurants and farms.||EPA Tailoring Rule|
|December 2010||EPA issued guidance to states on implementing the new GHG guidelines.||EPA Fact Sheet|
|January 2011||New GHG air permitting began for facilities that would have to go through air permitting for non-GHG pollutants anyway.||EPA GHG Permitting Fact Sheet|
|January 2011||EPA proposed a three-year deferral of GHG permitting for facilities that use biomass.||EPA Press Release|
|July 2011||New GHG permitting began for new facilities that would emit more than 100,000 tons of carbon dioxide equivalent per year and for facilities that will undergo major modification that would increase emissions by 75,000 tons of carbon dioxide equivalent per year||EPA Tailoring Rule Fact Sheet|
|July 2011||EPA finalized a three-year deferral of GHG permitting for facilities that use biomass.||EPA Biogenic Fact Sheet|
|September 2011||EPA will[when?] propose GHG guidelines under the “New Source Performance Standards” (NSPS), which will establish emission levels for new and existing power plants.||Power Plant Settlement Agreement|
|December 2011||EPA will[when?] propose GHG NSPS standards for oil refineries.||Oil Refinery Settlement Agreement|
|March 2012||EPA proposed carbon pollution standards for new power plants||EPA Fact Sheet|
|May 2012||EPA will issue final GHG standards for powerplants.||EPA Settlement Fact Sheet|
|November 2012||EPA will issue final GHG standards for oil refineries.||Oil Refinery Settlement Agreement|
|April 2015||EPA will complete study to examine GHG permitting for smaller sources of emissions.|
Contributors to, and the Consequences of, Climate Change
Physical and Social Contributors to the Problem of Climate Change
- “Suddenly, combustion of fossil fuels for transportation, power generation, industrial processes, and heating our homes has been abruptly transformed from a great solution to a huge problem…. We have based our cities, or businesses, and our lifestyle on the convenience and relatively low cost of gasoline, coal-fired electricity, and plastic. It’s no wonder that the specter of global warming appears so devastating: it threatens the roots of our culture.”
While there is a general consensus among the scientific community that anthropogenic GHG emissions are forcing changes in the global climate system, there is much less agreement about what should be done to address the problem because both the causes and potential solutions involve significant economic, political, and as Ingrid Kelley points out, social and cultural issues. Addressing climate change has been, and will continue to be particularly difficult for the United States because the U.S. was born during the Industrial Revolution and its growth has been powered by fossil fuels. Coal, for example, was first commercially mined in the United States in 1748, and within a few years after the ratification of the U.S. Constitution, Pittsburgh became the first industrial center in the country to use coal-fired steam power in its manufacturing operations. Electric generating plants first used pulverized coal in 1918, and that same basic method of generation is still in use today. In 2009, coal was used to produce 45% of electricity in the U.S. and that proportion is projected to remain more or less constant through 2035. Largely because of the Country’s reliance on coal, electricity generation accounted for 34% of U.S. GHG emissions in 2007, followed by transportation sources (28%) and other industrial sources (19%). In 2005, the United States emitted 18% of the world’s total GHG emissions, making it the second largest emitter after China. While the technology that powers our “fossil fuel culture” is part of the climate change problem, and more sustainable technologies will undoubtedly be part of the solution, another important factor in our efforts to stop climate change is the “blindness” that our economic system exhibits toward environmental degradation.
According to Al Gore, “[f]ree market capitalist economics is arguably the most powerful tool used by civilization” but it is also, “the single most powerful force behind what seem to be irrational decisions about the global environment.” The force to which Gore refers draws strength from the fact that environmental amenities such as clean air and other public goods do not have a price tag and are feely shared by everyone. The lack of price mechanisms to signal the scarcity of such goods means there are no economic incentives to conserve them. In what is known as the tragedy of the commons, rational individuals are motivated to over-utilize these resources for short-term economic gain despite the potential for collective action to deplete the resource or result in other adverse consequences in the long run. What this means for GHGs is that their effects on climate stability are often disregarded in economic analyses as externalities. As a frequently used measure of a country’s well being, the GDP, for example, places value on the goods and services produced within a country but fails to account for the GHG emissions and other environmental effects created in the process. Nations are thus incentivized to utilize their resources and promote consumption at ever increasing rates despite the consequences of those actions on atmospheric concentrations of GHGs and climate stability. In this respect, the ongoing UN climate change negotiations are fundamentally about the economic future of the nations involved.
EPA’s Finding that Greenhouse Gases Endanger Public Health and Welfare
- that six greenhouse gases in the atmosphere – CO2, CH4, N2O, hydrofluorocarbons, perfluorocarbons, and sulfur hexafluoride – may reasonably be anticipated to endanger both public health and public welfare; and
- that GHG emissions from mobile sources covered under CAA section 202(a) contribute to the total greenhouse gas air pollution, and thus to the problem of climate change.
In the Agency’s view, the body of work produced by the IPCC, the U.S. Global Change Research Program, and the National Research Council of the U.S. National Academy of Sciences represents the most comprehensive, advanced, and thoroughly reviewed documents on the science of climate change. Accordingly, the Administrator relied primarily upon assessment reports and other scientific documents produced by these entities in reaching her conclusions.
The IPCC defines “climate change” as “a change in the state of the climate that can be identified (e.g. using statistical tests) by changes in the mean and/or the variability of its properties, and that persists for an extended period, typically decades or longer. It refers to any change in climate over time, whether due to natural variability or as a result of human activity.” In its latest assessment on climate change, the IPCC found that “warming of the climate system is unequivocal” and that the anthropogenic component of this warming over the last thirty years has likely had a discernible influence on observed changes in many physical and biological systems. The properties of greenhouse gases are such that they retain heat in the atmosphere, which would otherwise escape to space. GHGs accumulate in the atmosphere when they are emitted faster than they can be naturally removed, and that accumulation prompts changes in the climate system. Once emitted into the atmosphere, GHGs influence the Earth’s energy balance for a period of decades to centuries. Consistent with their long-lasting impacts, the IPCC found that even if the concentrations of all GHGs had been kept constant at year 2000 levels, a further warming of approximately 0.1oC per decade would be expected. The fact that GHGs are long-lived in the atmosphere also means that they become well mixed across the globe – hence the global nature of the problem.
After considering the scientific evidence before her, Administrator Jackson found that greenhouse gases could be reasonably anticipated to endanger the health of the U.S. population in several ways. They are:
- Direct temperature effects - Heat is the leading cause of weather-related deaths in the U.S. and severe heat waves are projected to intensify over the portions of the country where these events already occur.
- Effects on air quality – Ground level ozone (the main component of smog) can induce chest pain, coughing, throat irritation, and congestion, and it can exacerbate respiratory illnesses such as bronchitis, emphysema, and asthma. Elevated temperatures associated with climate change are expected to intensify ground level ozone formation in polluted areas of the U.S.
- Effects on extreme weather events – The IPCC reports evidence of an increase in intense tropical cyclone activity in the North Atlantic since approximately 1970. Increases in tropical cyclone intensity are associated with increased death, injury, water- and food-borne disease, and post-traumatic stress disorder.
- Effects on climate-sensitive diseases – Expected changes in the climate will likely increase the spread of food- and water-borne pathogens among susceptible populations.
Administrator Jackson also found that GHGs could be reasonably anticipated to endanger public welfare in the following ways:
- Agriculture – While higher atmospheric CO2 concentrations may stimulate plant growth, climatic changes may also promote the spread of pests and weeds, increase ground level ozone formation (which is detrimental to plant life), and change temperature and precipitation patterns. Uncertainty remains about the extent to which these factors will balance each other but the evidence suggests a net disbenefit, with the potential for future crop failure.
- Forestry – As with agriculture, uncertainties remain but there is evidence of an increase in the size and occurrence of wildfires, insect outbreaks, and tree mortality in parts of the U.S. These effects are expected to continue with future changes in climate.
- Water resources – The effects of climate change on the water cycle have already been observed. For example, there is “well-documented evidence of shrinking snowpack due to warming” in the western U.S. These changes in snowfall are likely to affect areas such as California that rely on snowmelt for their water supply. Climate change is also expected to impact the water supply in other areas of the country, increasing competition for its use.
- Sea level rise – The greatest risk to the U.S. associated with sea level rise is the extent to which it will exacerbate storm-surge flooding. Areas along the Atlantic and Gulf coasts including New Orleans, Miami, and New York City are particularly vulnerable to such effects.
- Energy – Climate change is expected to increase peak electricity demand. This may further constrain water resources as power plants rely heavily on water for cooling. A large portion of U.S. energy infrastructure is located in coastal areas and may be at risk to damage from flooding.
- Ecosystems and wildlife – Changes in habitat range, timing of migration, and reproductive behavior have already been observed and are expected to increase with further warming. Ocean warming and acidification are expected to impair marine species such as corals, and the loss of arctic sea ice will reduce habitat for a number of species. Spruce-fir forests are, “likely to disappear from the contiguous United States.”
Regulatory Approaches Under the Clean Air Act for Reducing Greenhouse Gas Emissions
The Regulation of Greenhouse Gases from Mobile Sources
The Light-Duty Vehicle Greenhouse Gas Emission Standards and Corporate Average Fuel Economy Standards Rule
EPA’s endangerment finding in 2009 did not impose any limitations on GHGs by itself, but was instead a prerequisite for establishing regulations for GHGs from mobile sources under CAA section 202(a). Actual emissions requirements came later on May 7, 2010 when the EPA and the National Highway Traffic Safety Administration finalized the Light-Duty Vehicle Greenhouse Gas Emission Standards and Corporate Average Fuel Economy Standards Rule (LDV Rule). The LDV Rule applies to light-duty vehicles, light-duty trucks, and medium-duty passenger vehicles (e.g., cars, sport utility vehicles, minivans, and pickup trucks used for personal transportation) for model years 2012 through 2016. The EPA estimated that this rule will prevent 960 million metric tons of CO2-equivalent emissions from being emitted to the atmosphere, and that it will save 1.8 billion barrels of oil over the lifetime of the vehicles subject to the rule.
The LDV Rule accomplishes its objectives primarily through a traditional command-and-control approach. The most substantial requirements come in the form of two separate CO2 standards (one for cars and the other for trucks, expressed on a gram per mile basis) that apply to a manufacturer’s fleet of vehicles. To determine compliance with the requirements of the rule, manufacturers must calculate a production-weighted fleet average emissions rate at the end of a model year and compare it to a fleet average emission standard. The emission standard for a manufacturer in a given model year is calculated based on the footprints of the vehicles in its fleet and the number of vehicles produced by the manufacturer at each footprint. The standards are designed so that they gradually become more stringent each year from 2012 to 2016. The LDV Rule also includes standards of 0.010 gram/mile and 0.030 gram/mile for N2O and CH4, respectively. These standards were primarily put in place as an anti-backsliding measure as N2O and CH4 are already emitted from motor vehicles in relatively low amounts.
Although prescriptive regulation is among the most common policy approaches for environmental regulation, it is not without its drawbacks. Prescriptive regulations are often criticized, for example, as being overly rigid and uneconomical because they do not necessarily encourage regulated entities to reduce emissions beyond the minimum standards and they may not achieve the intended benefits at the lowest possible cost. The LDV Rule addresses these criticisms in a number of ways. First, as noted above, the emissions standards gradually become more stringent over time. This not only prevents stagnation that might occur with a single standard, it gives manufacturers sufficient lead time to adapt to the most stringent requirements. In addition, the LDV Rule includes a number of regulatory flexibilities, the most significant of which is a program that allows for banking and trading of credits. In general terms, the LDV Rule allows manufacturers to bank emissions credits in instances where their fleet average CO2 emissions are less than the applicable standard. Manufacturers can then use the credits themselves where certain vehicle models fall short of the standard, or they can sell the credits to another manufacturer. According to EPA, these banking and trading provisions promote the environmental objectives of the rule by addressing issues associated with technological feasibility, lead time, and cost of compliance with the standards.
State Regulation of Greenhouse Gases from Motor Vehicles
With one exception, the responsibility for regulating emissions from new motor vehicles under the CAA rests with the EPA. Section 209(a) of the Act states in part: “No state or any political subdivision thereof shall adopt or attempt to enforce any standard relating to the control of emissions from new motor vehicles or new motor vehicle engines subject to this part.” Section 209(b) of the Act provides for the exception; it grants the EPA the authority to waive this prohibition for any state that had adopted emissions standards for new motor vehicles or engines prior to March 30, 1966. California is the only state that meets this eligibility requirement and is thus the only state in the nation, which can seek to obtain a waiver from the EPA. In order to obtain a waiver and establish its own emissions requirements, the State must demonstrate, among other things, that its standards will be at least as protective as public health as any applicable federal standards. Once California obtains a waiver for a particular standard, other states may generally adopt that standard as their own.
On September 24, 2004, the California Air Resources Board (CARB) adopted emissions standards for GHGs from new passenger cars, light-duty trucks and medium-duty vehicles. Not unlike the LDV Rule, California’s regulations establish standards for CO2 equivalent emissions from two classes of vehicles on a gram per mile basis. Also like those in the LDV Rule, California’s standards become more stringent over time. CARB initially requested a waiver from EPA for these standards on December 21, 2005. EPA denied that request on March 6, 2008, stating that the State did not need the standards to address compelling and extraordinary conditions (as is required by CAA section 209(b)(1)(B)) because the effects of climate change in California were not extraordinary compared to the effects in the rest of the country. Upon reconsideration, EPA later withdrew its previous denial and approved California’s waiver request on July 8, 2009. Fifteen states have adopted California’s standards. Further, California and EPA have worked together so that the two programs converge and allow automakers to produce a single national fleet, which complies with both programs.
The Regulation of Greenhouse Gases from Stationary Sources
“New Source Review” (NSR) is a permitting program established by the CAA, which requires the owners or operators of “major” stationary sources of air pollution to obtain permits prior to the construction or modification of those sources. The major source NSR program has two parts:
- the Prevention of Significant Deterioration (PSD) Program, which applies to a) sources located in areas of the country that meet the National Ambient Air Quality Standards (NAAQS), and b) to pollutants for which there are no NAAQS; and
- the Nonattainment New Source Review (NNSR) program, which applies to sources located in areas that do not meet the NAAQS.
PSD permits are issued by EPA or a state or local government agency, depending on who has jurisdiction over the area in which the facility is located. In order to obtain a PSD permit, applicants must demonstrate that the proposed new major source, or major modification to an existing source, meets several regulatory requirements. Among those requirements are the use of the Best Available Control Technology (BACT) to limit air pollutant emissions, and a demonstration through air quality modeling that the source or modification will not cause or contribute to a violation of the NAAQS.
Under federal regulations, the PSD program applies only to sources that emit one or more “regulated NSR pollutants.” In 2008, EPA Administrator Stephen Johnson issued a memorandum to document the Agency’s interpretation of this regulatory text. In particular, Administrator Johnson stated that a pollutant becomes a “regulated NSR pollutant” when a provision of the Act, or regulations established under the Act, require actual control of that pollutant but not when the Act or such regulations simply require monitoring or reporting of emissions of that pollutant. Upon request to reconsider this interpretation, EPA Administrator Lisa Jackson confirmed that that Agency would continue to apply the interpretation expressed in the 2008 memorandum but she further clarified that the time at which a pollutant becomes a “regulated NSR pollutant” is when the requirements that control emissions of the pollutant take effect, rather than upon the promulgation of those requirements. Because the LDV Rule requires vehicle manufacturers to meet applicable GHG standards for model year 2012 vehicles, and January 2, 2011 is the first day upon which model year 2012 vehicles can be introduced into commerce, the six GHGs regulated by that rule became regulated NSR pollutants as of January 2, 2011 for purposes of the PSD program.
Among the components of the PSD program, the one that primarily applies to GHGs is the requirement that source owners or operators utilize BACT to limit GHG emissions from the source. Permitting authorities generally establish BACT through a five-step analytical process, the end result of which is the selection of one or more methods to reduce emissions of the pollutant in question, and the setting of one or more emission limits and operational restrictions for the emissions units undergoing review. Because the PSD program and its requirement to utilize BACT apply to any new source or modification at an existing source that meets established applicability criteria, the PSD program represents a traditional command-and-control approach to the regulation of GHGs. However, BACT is established by a permitting authority on a case-by-case basis considering site- and source-specific factors. During the course of a BACT analysis, a permitting authority may, for example, temper the stringency of the final emission limit if there are compelling adverse economic, energy, or environmental considerations.
The PSD program is complex, and obtaining a permit can be costly for both the applicant and the permitting authority. It has been estimated, for example, that permit applicants expend 866 hours of labor and $125,120 on the average PSD permit. The administrative cost to the permitting authority for the same permit is 301 hours of labor and $23,280. Traditionally, this permitting process has been focused on controlling emissions from large industrial sources of air pollution such as fossil fuel-fired power plants, petroleum refineries, and a wide range of manufacturing plants that emit more than 250 tons per year of the regulated pollutants (in some cases the applicability threshold is 100 tons per year). Prior to the regulation of GHGs under the CAA, approximately 280 such permits were issued each year. However, GHGs are generally emitted from sources in amounts far greater than other pollutants regulated under the PSD program. So much so, that sources like office buildings and large shopping malls could easily cross the 250 ton per year threshold and become subject to PSD permitting requirements. In fact, without any action to change how the PSD program is applied, the EPA estimated that as many as 41,000 sources may require permits every year with the addition of GHGs as a regulated pollutant. To prevent the unbearable administrative burdens on permitting authorities associated with such “absurd results,” the EPA took action on June 3, 2010 to modify the applicability criteria in the PSD regulations. This action is known as the Prevention of Significant Deterioration and Title V Greenhouse Gas Tailoring Rule (Tailoring Rule). Through the Tailoring Rule, EPA raised the major source regulatory threshold for GHGs from the 100/250 ton per year levels to 100,000 tons per year of CO2 equivalent emissions, and this was declared unconstitutional by the Supreme Court.
The Suitability of the Clean Air Act for Regulating Greenhouse Gases
Because the LDV Rule and the application of the PSD program to GHGs took effect only recently, it is too soon to assess by how much they have reduced actual GHG emissions and at what cost. However, given the tremendous implications that regulation of GHGs has for almost every aspect of our society, it should not be surprising that much has already been written about the adequacy of the CAA for regulating global pollutants. It should also be no surprise that opinions on this question are widely varied. Allen and Lewis, for example, contend the CAA is wholly unsuitable for regulating GHGs because it was not designed to do so and the costs of such regulation potentially far exceed the costs associated with climate change legislation recently considered in Congress. As support for their argument that the CAA is a poor fit for GHGs, they point to the “absurd results” that EPA itself acknowledged and sought to avoid through passage of the Tailoring Rule:
- “EPA is entirely correct: Congress did not intend to apply PSD and Title V to small entities, did not intend for those programs to crash under their own weight, and did not intend for PSD to stifle economic growth. [footnote omitted] And Congress never intended for EPA to control CO2 emissions under the CAA! [footnote omitted] Congressional support for regulatory climate policy is much stronger today than it was in 1970 and 1977, when Congress enacted and amended CAA section 202. [footnote omitted] Yet even today, the prospects for cap-and-trade legislation and for U.S. ratification of a successor treaty to the Kyoto Protocol remain in doubt. [footnote omitted] The notion that Congress, in 1970 or 1977, implicitly authorized EPA to adopt economy-wide, or even industry-specific, controls on CO2 is ludicrously unfounded. [footnote omitted]”
Economists Dallas Burtraw and Arthur G. Fraas with the nonprofit and nonpartisan research organization Resources for the Future offer a different perspective on the subject of GHG regulation under the CAA. Although they agree that new legislation specifically designed to address climate change is the best long-term option, they characterize the CAA as a, “potentially potent alternative” in the absence of such legislation for the short-term. They note, for example, that EPA has already identified improvements in energy efficiency as the most attractive short-term option for mitigating GHGs at existing facilities in many industrial sectors. They go on to state that such improvements would most likely be among the first moves made by regulated entities under a legislative approach so it is unlikely that requiring these moves through regulation would result in comparatively higher costs. Based on their research, they conclude that domestic GHG reductions of up to 10% relative to 2005 levels could be achieved at moderate costs, which is comparable to reductions that would have been achieved under the Waxman-Markey climate change bill that was passed by the House of Representatives in 2009. In their view, the success of regulating GHGs under the CAA as it exists today rests with the EPA:
- “We see substantial opportunities under the Clean Air Act for domestic emissions reductions that can be achieved at what will probably be moderate cost. However, enthusiasm about the act as a vehicle for carbon regulation should be tempered. First, this paper suggests that achieving meaningful emissions benefits at reasonable cost is possible, but it will require EPA to be bold. The agency must interpret sections of the act to enable use of flexible mechanisms, must be ambitious in setting emissions targets, and must shift its focus to a new regulatory program. In short, to do all of this well, the agency will need to innovate…. Second, EPA action under the CAA is inferior to new legislation from Congress, especially over the long term. Although it is possible to identify some readily available opportunities for emissions reductions and push them via regulation (with market tools to keep costs down), it quickly becomes difficult to identify what steps should be taken next…. With those reservations, however, the Clean Air Act—if used wisely by EPA—can be a useful vehicle for short-term greenhouse gas regulation.”
The Influence of Stakeholders in Shaping How Greenhouse Gases Are Regulated Under the Clean Air Act
Because EPA’s authority to regulate GHG emissions has such significant implications for the economy, the environment, and our society at large, it is a topic of interest to a broad range of organizations including Congress, the courts, the states, environmental organizations, and the regulated industry. All of these entities have had a direct hand in shaping the laws, regulations, and policies concerning GHGs into what they are today and will likely continue to do so in the future. As discussed above, California has played a large role in shaping the motor vehicle regulations. EPA’s authority to regulate GHGs under the CAA is also a topic of continuing political debate in both chambers of Congress. On January 21, 2010, Senator Lisa Murkowski (R-AK) introduced a disapproval resolution under the Congressional Review Act, which would have nullified EPA’s endangerment finding. The resolution was defeated by a vote of 53-47, with six democrats voting in favor of it. Later that year on March 4, Senator Jay Rockefeller (D-WV) introduced a bill that would suspend for two years any EPA action to regulate CO2 or CH4 under the CAA except for the vehicle standards under section 202. He re-introduced similar legislation on January 31, 2011, the same day Senator John Barrasso (R-WY) introduced broad legislation to preempt regulation of GHGs under federal law. On February 2, 2011, Representative Fred Upton (R-MI), Representative Ed Whitfield (R-KY), and Senator James Inhofe (R-OK) released a draft bill, which would amend the CAA to, “prohibit the Administrator of the Environmental Protection Agency from promulgating any regulation concerning, taking action relating to, or taking into consideration the emission of a greenhouse gas due to concerns regarding possible climate change, and for other purposes.”
That the major opposition to regulation of GHGs under the CAA is headed largely by a contingent of elected officials from major coal, oil, and gas states exemplifies the political warfare that can erupt when leaders attempt to appeal to their core constituencies even though doing so may impede action on pressing national problems. It also underscores Al Gore’s view that the political system will be the “decisive factor” in our efforts to address global climate change: “the real work must be done by individuals, and politicians need to assist citizens in their efforts to make new and necessary choices.” Whether Congress will act any time soon to pass cap-and-trade legislation or revoke EPA’s authority to regulate GHGs is questionable. However, even inaction by Congress in this area leaves EPA’s future options open.
In his book Earth in the Balance, Al Gore observes that, “the American people often give their leaders permission to take action [on an issue] by signaling agreement in principle while reserving the right to object strenuously to each and every specific sacrifice necessary to follow through.” As a recent illustration of Gore’s point, consider the results of a public opinion poll conducted in June 2010. One thousand people were asked the question: “How important is the issue of global warming to you personally?” Seventy six percent of respondents said they considered global warming to be extremely important, very important, or somewhat important. Sixty eight percent of people in the same survey also said that the United States should take action on global warming even if other major industrial countries such as China and India do not agree to do equally effective things. However, when asked, “[P]lease tell me whether you favor or oppose the federal government…[increasing] taxes on gasoline so people either drive less, or buy cars that use less gas,” seventy one percent of the survey respondents said they opposed increased gasoline taxes, despite the fact that such a tax would be “one of the logical first steps” we would likely take in an effort to reduce oil consumption and address climate change. Thus, there is an apparent discrepancy between the public’s feelings about the threat of climate change and its willingness to make personal sacrifices to address it. The reluctance of both the American public and Congress to make sometimes difficult choices to address climate change has left opportunities wide open for other stakeholders to influence climate change policy; among the most influential thus far are non-governmental organizations (NGOs).
In his article, “Learning to Live with NGOs,” P.J. Simmons wrote that NGOs can, “make the impossible possible by doing what governments cannot or will not.” History shows that this is particularly true where climate change regulation is concerned. While NGOs cannot themselves pass climate change regulations, they have played a clear role in forcing EPA’s hand through action in the courts. EPA’s endangerment finding, the LDV Rule, and the consequent regulation of GHGs from stationary sources under the PSD program are a direct result of the Supreme Court’s decision in Massachusetts v. EPA. As discussed supra, that case is founded on the petition submitted to EPA in 1999 by the International Center for Technology Assessment and nineteen other NGOs. With passage of the LDV Rule, EPA did what ICTA and its fellow petitioners demanded more than ten years earlier. And a number of NGOs have continued to apply pressure to EPA. On December 23, 2010, EPA announced that it would establish GHG standards for new and modified electric generating units (EGUs) and petroleum refineries under section 111(b) of the CAA, and that it would set GHG emissions guidelines for existing sources in those same categories under CAA section 111(d); these emissions standards and guidelines will be established according to a schedule set forth in settlement agreements into which EPA entered to settle legal challenges brought forth by several NGOs and states after EPA failed to establish GHG standards when it revised its rules for EGUs and refineries in 2006 and 2008. Under the terms of the agreement, EPA will issue final standards for EGUs and refineries in May 2012 and November 2012, respectively.
EPA’s actions to address climate change are also being challenged by those most directly affected – the regulated community. Over eighty claims have been filed by thirty-five different petitioners against EPA related to the endangerment finding, the LDV Rule, the Tailoring Rule, and another rule related to the PSD program. A large number of the parties in these cases are businesses and industry associations (acting in the interests of businesses) such as Peabody Energy Company, Gerdau Ameristeel U.S. Inc., Coalition for Responsible Regulation, National Association of Manufacturers, Portland Cement Association, National Mining Association, American Farm Bureau Association, and the U.S. Chamber of Commerce. These claims have been consolidated into Coalition for Responsible Regulation v. U.S. Environmental Protection Agency (CRR v. EPA) under three main docket numbers, 09-1322, 10-1092, and 10-1073. The arguments put forth by the plaintiffs are numerous and varied, depending on the particular case but most are fundamentally about the economic impacts of regulation. A summary of the arguments has been compiled by Gregory Wannier of The Center for Climate Change Law at the Columbia Law School. On June 26, 2012, the Court of Appeals for the District of Columbia Circuit issued an opinion in CRR v. EPA which dismissed the challenges in these cases to the EPA's endangerment finding and the related GHG regulations. The three-judge panel unanimously upheld the EPA's central finding that GHG such as carbon dioxide endanger public health and were likely responsible for the global warming experienced over the past half century.
- Court Backs E.P.A. Over Emissions Limits Intended to Reduce Global Warming June 26, 2012
- D.C. appeals court upholds EPA regulations to fight global warming by Darryl Fears, June 26, 2012
- 42 U.S.C. § 4521(a)(1). Retrieved from http://www.law.cornell.edu/uscode/html/uscode42/usc_sec_42_00007521----000-.html
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