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IB10004: Clean Air Act Issues in the 106th CongressJames E. McCarthyResources, Science, and Industry Division November 14, 2000CONTENTS
Congress last enacted major amendments to the Clean Air Act in 1990, and the Environmental Protection Agency (EPA) is still implementing numerous provisions of those amendments. Recent efforts include the start of Phase 2 of the reformulated gasoline program, proposal of tighter emission standards for diesel engines and related standards for sulfur in diesel fuel, new programs to control ozone transport, implementation of controls on sources of 188 air toxics, and review of state implementation plans for attaining ozone standards. EPA decisions regarding these and other programs will provide opportunities for oversight in the remaining days of the 106th Congress and in the 107th Congress as well. On the legislative front, bills to diminish the use of MTBE, a gasoline additive, have been at the top of the clean air agenda. MTBE is used to meet Clean Air Act requirements that gasoline sold in the nation's worst ozone nonattainment areas contain at least 2% oxygen. The additive has been implicated in numerous incidents of ground water contamination. On September 28, 2000, the Senate Environment and Public Works Committee reported S. 2962 to ban MTBE use, waive the oxygen requirement, and provide additional funding for ground water cleanup (S.Rept. 106-426), but no further action has been taken. Of particular concern are the potential impacts of any such legislation on the use of another oxygenate, ethanol, made largely from corn: the reported bill provides regulatory requirements that could triple ethanol use over the next decade. The Clean Air Act and its 1990 amendments appear to have contributed to a marked improvement in air quality nationwide. Of nearly 100 metropolitan areas not meeting air quality standards for ozone in 1990, more than two-thirds now do so. Even greater progress has been achieved with carbon monoxide: 36 of 42 areas not in attainment in 1990 now meet the standard. Nevertheless, EPA remains concerned about air pollution. In 1997, the Agency promulgated major revisions to its air quality standards for ozone and particulates, an action that would require most states and urban areas to establish additional controls on a wide range of pollution sources. The revised standards were challenged by numerous parties and the courts have remanded the standards to EPA. Implementation is currently in limbo, pending resolution of appeals by the Supreme Court. Other issues in which Congress has expressed an interest include how and whether to control long-distance ozone transport, including the desirability of additional regulation for sources of nitrogen oxides such as electric utilities, and whether plans for new highways must conform to emission budgets under the Clean Air Act. Note: This Issue Brief does not discuss the "greenhouse effect" or issues related to global climate change. For a discussion of those issues, see CRS Issue Brief IB89005, Global Climate Change, updated regularly. On October 27, 2000, the President signed H.R. 4635 (P.L. 106-377), the VA-HUD-Independent Agencies appropriation for FY2001. The bill prohibits the Environmental Protection Agency from designating ozone nonattainment areas prior to a decision by the Supreme Court in American Trucking Associations v. EPA, or June 15, 2001, whichever occurs first. The action was intended to prohibit the Agency from moving forward with implementation of its new 8-hour ozone standard before the Supreme Court decides a case challenging the Agency's authority to promulgate the standards. Oral arguments in the case were heard November 7. The appropriation bill also delays for one year the application of transportation conformity requirements after any such areas are designated. On September 28, 2000, the Senate Environment and Public Works Committee reported S. 2962 to ban MTBE use, waive the reformulated gasoline program's oxygen requirement, and provide additional funding for ground water cleanup (S.Rept. 106-426). The bill is intended to address problems caused by MTBE contamination of ground and surface water in numerous areas. On August 30, the Court of Appeals for the D.C. Circuit granted an additional 13 months for utilities and others to comply with what is called the NOx SIP call, or Ozone Transport Rule. The rule will require power plants in the Midwest and Southeast to install controls to prevent the transport of pollution to the Northeast. The court upheld EPA's authority to issue the rules earlier this year. The Clean Air Act requires the Environmental Protection Agency (EPA) to establish minimum national standards for air quality, and assigns primary responsibility to the states to assure compliance. Areas not meeting the standards, referred to as nonattainment areas, are required to implement specified air pollution control measures. The Act establishes federal standards for autos and other mobile sources of air pollution, for sources of 188 hazardous air pollutants, and for the emissions that cause acid rain. It establishes a comprehensive state-run permit system for all major sources of air pollution. It also addresses the prevention of pollution in areas with clean air, as well as protection of the stratospheric ozone layer. The last comprehensive amendments to the Act, enacted November 15, 1990 (P.L. 101-549), included the program to control acid rain, new standards for emissions of hazardous air pollutants, new requirements for motor vehicles and fuels, and stringent new requirements for nonattainment areas. Many of these provisions (notably the acid rain and air toxics provisions, and some of the requirements for autos and fuels) were strenuously debated, but most have not been subject to controversy since enactment. The new provisions on acid rain, air toxics, and automobiles have generally been implemented on schedule, in many cases at less cost than anticipated. There have also been noticeable improvements in air quality in recent years: of 98 metropolitan areas not attaining the 1-hour ozone standard in 1990, two-thirds now do so. Even greater progress has been achieved with carbon monoxide: 36 of the 42 areas not in attainment in 1990 now meet the standard. Nevertheless, major controversies remain concerning implementation of the Act. MTBE and Reformulated Gasoline Under the Clean Air Act Amendments of 1990, numerous areas with poor air quality are required to add chemicals called "oxygenates" to gasoline as a means of improving combustion and reducing emissions. The Act has two programs that require the use of oxygenates, but the more significant of the two is the reformulated gasoline (RFG) program, which took effect January 1, 1995. Under the RFG program, areas with "severe" or "extreme" ozone pollution (82 counties with a combined population of 55 million) must use reformulated gas; areas with less severe ozone pollution may opt into the program as well, and many have. In all, portions of 17 states and the District of Columbia use RFG, and a little more than 30% of the gasoline sold in the United States is RFG. The law requires that RFG contain at least 2% oxygen by weight. Refiners can meet this requirement by adding a number of ethers or alcohols, any of which contain oxygen and other elements. By far the most commonly used oxygenate is MTBE. In 1999, 87% of RFG contained MTBE. MTBE has also been used since the late 1970s in non-reformulated gasoline, as an octane enhancer, at lower concentrations. As a result, gasoline with MTBE has been used virtually everywhere in the United States, whether or not an area has been subject to RFG requirements. State and local environmental agencies and EPA attribute marked improvements in air quality to the use of oxygenated and reformulated gasoline. The improvements in air quality have not come without controversy. In Alaska and Wisconsin, residents complained of a wide array of effects, including headaches, dizziness, nausea, sore eyes, and respiratory irritation, from exposure to gasoline/MTBE exhaust, before refiners switched to alternative gasoline formulations using ethanol. MTBE from a number of sources, including leaking underground storage tanks, has also been linked to contamination of drinking water supplies. For a variety of reasons, concerns over MTBE have focused on California for much of the past three years. California has the most extensive reformulated gasoline requirements in the country, with state requirements separate and in addition to the federal. In addition, it has experienced the most significant contamination of drinking water by MTBE. The incidents of drinking water contamination led the state legislature in October 1997 to enact legislation to require state standards for MTBE in drinking water and to require the University of California (UC) to conduct a study of the health and environmental effects of MTBE. The UC report, issued in November 1998, recommended a gradual phase-out of MTBE use in the state. Based on the report and on subsequent public hearings, on March 25, 1999, Governor Davis of California signed an Executive Order to require a phase-out of MTBE use in the state by December 31, 2002, and requested a waiver of federal requirements to use oxygenates in reformulated gasoline. (Seven other states - Iowa, Arizona, Colorado, New York, Connecticut, Michigan, and Minnesota - have subsequently passed legislation to limit or phase out MTBE.) The California request for a waiver of the oxygen requirement has resulted in months of negotiation between EPA and the state, with EPA initially expressing skepticism that it had authority to grant a waiver under the circumstances. A decision on the request is still awaited. Without a waiver, ozone nonattainment areas in the state would be required to substitute another oxygenate (most likely, ethanol) when the MTBE ban takes effect. The MTBE issue received additional attention in July 1999, when an advisory panel reported to EPA Administrator Carol Browner. The Blue-Ribbon Panel on Oxygenate Use in Gasoline, composed of industry representatives, state and local officials, environmentalists, academics, and others, recommended that Congress remove the RFG program's oxygenate requirement and clarify state authority to regulate gasoline components. Subsequently, on August 4, 1999, the Senate adopted by voice vote Senator Boxer's amendment to the FY2000 Agriculture appropriations bill (S. 1233) expressing the sense of the Senate that use of MTBE should be phased out. The principal issues for Congress are whether Clean Air Act provisions concerning oxygenate use in reformulated gasoline should be waived to allow refiners to discontinue or lessen their use of MTBE and whether stronger steps, such as a ban on MTBE use, should be considered. Legislation to provide a waiver for California refiners (H.R. 11 / S. 266) has the nearly unanimous support of that state's congressional delegation. The legislation would remove the oxygenate requirement for refiners and marketers of RFG provided that the fuel continues to meet all performance (i.e., emission reduction) standards. The bill would apply in California only -- not in other states. The House Commerce Subcommittee on Health and Environment approved H.R. 11, with an amendment, September 30, 1999. Amendments to phase out the use of MTBE, to apply the bill's provisions to areas outside California, and to address international trade issues related to MTBE phase-out were offered and withdrawn during markup, and might need to be addressed before the bill or a substitute would be considered by the full committee. A hearing on these issues was held March 2, 2000, by the Health and Environment Subcommittee. Separate legislation allowing additional flexibility in all states has also been introduced, as have numerous bills that would phase-out or ban the use of MTBE in gasoline. (For additional discussion of the MTBE issue, see CRS Report 98-290, MTBE in Gasoline: Clean Air and Drinking Water Issues.) While support for waiving the oxygen requirement now seems to be widespread among environmental groups, the petroleum industry, and states, a potential obstacle to enacting legislation lies among agricultural interests. About 6% of the nation's corn crop is used to produce a competing oxygenate, ethanol. If MTBE use is reduced or phased out, but the oxygen requirement remains in effect, ethanol use would likely soar, increasing demand for corn. Conversely, if the oxygen requirement is waived by EPA or legislation, not only would MTBE use decline, but so, likely, would demand for ethanol. Thus, Members, Senators, and Governors from corn-growing states have taken a keen interest in MTBE legislation. Unless their interests are addressed, they might pose a potent obstacle to its passage. Reflecting these dual concerns, EPA Administrator Carol Browner and Agriculture Secretary Dan Glickman called on Congress at a press conference, March 20, 2000, to amend the Clean Air Act to "significantly reduce or eliminate" the use of MTBE and to require the use of ethanol in all gasoline. EPA also announced that it would begin the process of requiring a phase-out of MTBE under Section 6 of the Toxic Substances Control Act, a process likely to take "several years" in EPA's estimation. Legislation to mandate the use of ethanol while allowing limits on MTBE use (S. 2503 and S. 2971) was subsequently introduced, and Senator Smith of New Hampshire, Chairman of the Environment and Public Works Committee produced several drafts of legislation that would preserve a role for ethanol as well. On July 27, he introduced S. 2962. The committee ordered it reported with an amendment in the nature of a substitute on September 7. (The report [S.Rept. 106-426] was filed September 28.) As reported, the bill would give the EPA Administrator authority to phase down use of MTBE in gasoline. Whether or not the Administrator uses this authority, the bill would ban MTBE use within 4 years of enactment. The bill would allow Governors to waive the RFG program's oxygenate requirement, and would set new standards for toxic substance and aromatic content of RFG in areas where the waiver is exercised. It would stimulate the use of ethanol and clean vehicles: each fuel supplier would have the option of using an increasing percentage of renewable fuel (ethanol) in each year between 2002 and 2011, or could use credits generated by the manufacture and sale of zero emission or "super ultra low" emission vehicles. The report notes that this requirement could nearly triple the consumption of ethanol by 2011. The bill would provide additional authority to EPA to regulate fuel additives and emissions. It also would authorize a one-time appropriation of $200 million from the Leaking Underground Storage Tank Trust Fund to clean up MTBE leaks from tanks, and authorize another $200 million over 6 years for states to use to oversee and enforce tank leak prevention and detection regulations. Impact of Phase 2 of the RFG Program In June 2000, as consideration of alternatives to the use of MTBE took place, the requirements for reformulated gasoline were also changing and gasoline prices temporarily rose rapidly. Prices rose for a number of known reasons, including high crude oil prices, low U.S. inventories, and transportation bottlenecks due to operational difficulties experienced by two Midwestern pipelines. Some analysts argued that there was, at least in part, a cause and effect relationship between the changes in the RFG requirements (which took effect June 1) and the rise in gasoline prices. While there was some connection, the cost of meeting the new requirements does not appear to have been a significant factor in explaining the overall rise in prices. Administration estimates placed the increased cost of meeting RFG requirements at 2 to 8 cents per gallon -- 1-2 cents of which represented additional costs from the implementation of new requirements this year. Later changes in gasoline prices (including a sharp drop in wholesale RFG prices in the Chicago market starting June 15) appeared to confirm that the increased cost of RFG production played only a limited role in driving gasoline prices higher. (For a further discussion of the new "Phase 2" RFG requirements, see CRS Report 98-290, MTBE in Gasoline: Clean Air and Drinking Water Issues.) Regulation of Diesel Fuel / Emissions A new issue, on which a Senate Environment and Public Works subcommittee held oversight hearings in June and September, is the regulation of diesel fuel and diesel engine emissions. Diesel emissions have been among the least regulated major sources of air pollution. While automobiles have been required to reduce emissions more than 90% since the 1970s and face even tighter controls under standards promulgated February 10, 2000, diesel emissions have faced relatively few controls. On May 17, 2000, however, EPA began the process of changing this situation, proposing a greater than 90% reduction in allowable emissions from new diesel engines beginning in 2007. Because sulfur interferes with the effectiveness of the likely emission control technologies, the Agency also proposed a 97% reduction in the allowable sulfur content of diesel fuel, from 500 to 15 parts per million (ppm), effective in June 2006. The proposal appeared in the Federal Register June 2. Engine manufacturers are largely satisfied with the rule, but refiners, service station owners, and the trucking industry generally argue that achieving the proposed fuel standards would be difficult and costly, could likely result in refinery closures, and could cause shortages of diesel fuel. Instead of 15 ppm, trade associations representing refiners have backed a 50 ppm sulfur standard; EPA and the engine manufacturers say that would not be sufficiently stringent to permit optimal operation of pollution controls. EPA agrees that meeting the sulfur reduction standard will result in increased cost, but places the cost at 3-4 cents per gallon. As EPA's proposal noted, "The diesel engine is a vital workhorse in the United States, moving much of the nation's freight, and carrying out much of its farm, construction, and other labor." As a result, this proposal affects an unusually large number of economic sectors, and has generated substantial controversy. The Agency held five public hearings in New York, Chicago, Atlanta, Los Angeles, and Denver during the month of June, and took public comments until August 14. The Agency expects to finalize the rule in December. The Clean Air subcommittee of Senate Environment held hearings June 15 and September 21. Continued congressional oversight is considered likely. (See CRS Report RL30737 (pdf), Diesel Fuel and Engines: An Analysis of EPA's Proposed Regulations.) Under the Clean Air Act, there are two provisions that can result in denial of federal highway funding to local areas: sanctions and a lapse in what is called "conformity." The sanction authority is found in Sections 179 and 110(m) of the Act. Under these sections, the EPA Administrator is required to impose highway fund and other sanctions on areas 18 - 24 months after reaching a finding that an area has not submitted or not implemented adequate plans to attain air quality standards. The Act authorizes EPA to use two types of sanctions: 1) imposing what are called "2:1 offsets" on new or modified sources of emissions; and 2) withholding certain federal highway funds. Under the sanction regulations, EPA first imposes the offset sanction, 18 months after reaching a finding (unless the deficiency has been corrected). If the deficiency has still not been corrected 6 months later, both sanctions are applied. It is not failure to attain air quality standards that leads to sanctions, but failure to submit an acceptable plan or to implement the measures identified therein. When highway fund sanctions are imposed, not all funding is affected. Projects are exempt from sanctions when the Department of Transportation determines that the principal purpose is an improvement in safety. In addition, despite sanctions, DOT may approve several types of projects geared toward improvement of air quality, including transit projects, HOV lanes, breakdown lanes, projects to improve traffic flow, and park-and-ride lots. The threat of sanctions is a powerful tool; but, perhaps because the threat is powerful, the imposition is a rare event. Since 1990, only 2 areas have had highway sanctions imposed. Conformity requirements, found in Section 176 of the Act, have been invoked more frequently. This section prohibits federal departments and agencies from approving, permitting, or providing financial support to transportation improvements in areas that have not attained air quality standards, unless such improvements conform with the State Implementation Plan for achieving air quality. Conformity determinations are also a powerful tool -- one meant to integrate transportation and air quality planning. Areas in 29 states have experienced a lapse of conformity at some time since 1993, and 5 areas, the largest of which is Atlanta, currently have lapsed conformity. Conformity lapses operate in a fashion similar, in some respects, to highway fund sanctions. As with sanctions, exceptions are provided for highway projects that will improve safety or air quality. Further limiting their impact, conformity lapses have, until recently, been applied only to new projects. In many cases, an area simply waits until its next revision of its Transportation Improvement Program (TIP) or its State Implementation Plan to revise the proposed project or through other measures to return to conformity. Thus, until recently, few areas lost funding despite a conformity lapse. One reason that conformity has come to the attention of Congress in the past year and a half is a court decision: on March 2, 1999, the U.S. Court of Appeals for the District of Columbia Circuit ruled that the Clean Air Act limits grandfathering of funding in conformity situations, overturning EPA's regulations and considerably raising the stakes for Atlanta and other areas that are subject to a conformity lapse. EPA and the Department of Transportation subsequently reached agreement on procedures to implement the court's decision, and the Agency announced on April 16, 1999, that it would not appeal the decision. This decision and another case awaiting trial in Missouri aroused congressional interest in the sanctions and conformity issues. Two bills (Senator Bond's S. 495 and Representative Baker's H.R. 1626) would repeal the highway fund sanction provisions, and five other bills (Senator Bond's S. 1053, Representative Talent's H.R. 1876, Representative Linder's H.R. 3583, Representative Lewis's H.R. 3686, and Senator Cleland's S. 2088) would either restore the grandfather provisions of the conformity rule overturned by the March 1999 court ruling or provide funding to certain transportation projects during a conformity lapse. The Senate Environment and Public Works Committee held a hearing on the conformity issue July 14, 1999, and ordered S. 1053 reported, with substantial amendments, September 29, 1999. (The report, S.Rept. 106-228, was filed February 2, 2000.) As amended, the bill would restore the grandfather provisions in effect prior to the March 1999 court decision for a period of one year while EPA writes new regulations. The bill also stipulates that certain projects, including any project approved prior to the court decision, may be implemented even if conformity lapses. It establishes new requirements regarding approval of emissions budgets by EPA, allows the use of non-federal funds for right-of-way acquisition and highway design during periods of conformity lapse, and delays the application of conformity to areas that may be designated nonattainment under the pending 8-hour ozone standard. (For additional background, see CRS Report RL30131 (pdf), Highway Fund Sanctions and Conformity Under the Clean Air Act, updated October 15, 1999.) While not the subject of legislation in this Congress, another subject of concern is the ozone transport rule promulgated by EPA on October 27, 1998, and subsequent EPA actions related to ozone transport. The rule, a major element of the ongoing effort to reduce ozone concentrations in the Northeastern states, implements a regional strategy for reductions in emissions of NOx, a pollutant that combines with volatile organic compounds to form ozone in areas downwind of its release. The ozone transport rule grew out of the efforts of the Ozone Transport Assessment Group (OTAG) to develop a regional strategy for NOx reductions. In June 1997, OTAG (a group composed of the 37 easternmost states) completed its work, recommending regional measures to reduce NOx emissions, but specifying only a broad range rather than an agreed percentage for the targeted reductions. EPA promulgated its regulations implementing the OTAG recommendations on October 27, 1998, calling for average reductions of 28% in NOx emissions in 22 Eastern states and the District of Columbia (later revised to 25%). These reductions were to be implemented through State Implementation Plans, beginning in May 2003. The SIPs were to be submitted to EPA by September 30, 1999. The degree to which the regulations impose additional requirements on utilities and other sources of NOx is the prime area of controversy. The accuracy of the modeling used to determine the distribution of the needed reductions, the form of emissions trading to be allowed under the regulations, and the amount (or lack) of flexibility EPA will give to the states in planning reductions are other issues. Several states went to court, challenging EPA's authority to issue the transport rule, and the U.S. Court of Appeals for the D.C. Circuit issued an indefinite stay of the rule on May 25, 1999 (Michigan v. EPA). On March 3, 2000, however, the Court upheld EPA's authority to issue the rule. The stay on its implementation was subsequently lifted, June 22, with a new deadline for submission of State Implementation Plans in October 2000. Most recently, on August 30, the Court extended the deadline for compliance, from May 1, 2003, to May 31, 2004. While the Appeals Court decisions are subject to further appeal, it now appears likely that the rule will be implemented in something close to the form promulgated. In a related action, EPA has decided on an approach to what are referred to as the "Section 126 petitions." Under Section 126, any state or political subdivision may petition EPA for a finding that stationary sources in another state are significantly contributing to nonattainment problems in their state. In response to petitions from 8 Northeastern states, EPA found in April, 1999, that 19 Midwestern and Southern states (and D.C.) contributed to nonattainment problems in 6 of the petitioning states with respect to the 8-hour ozone standard, and 12 Midwestern and Southern states (and D.C.) contributed to nonattainment difficulties with respect to the 1-hour standard. Implementation of this finding was to be contingent and coordinated with the state's response to the Ozone Transport Rule (OTR). In June, 1999, however, in response to the court stay of the OTR, EPA announced its intention to decouple the Section 126 findings from the Ozone Transport Rule. EPA took final action on four Section 126 petitions December 17, 1999, imposing NOx control requirements on 392 stationary sources located in the 12 states and D.C. The required controls take effect in May 2003. The transport rule, Section 126 petitions, and other measures (both state and EPA lawsuits) aimed at reducing emissions from electric utilities have come to the attention of Members of Congress from some of the affected states, but there has been no action in the 106th Congress. (For additional information on the OTAG process and the promulgated rule, see CRS Report 98-236 (pdf), Air Quality: EPA's Ozone Transport Rule, OTAG, and Section 126 Petitions -- A Hazy Situation?) Implementation of the National Ambient Air Quality Standards Another issue that Congress has followed closely, but where much of the current focus of attention is in the courts, is that of the revised air quality standards promulgated by EPA in 1997. Under the Clean Air Act, EPA sets national standards for ambient (outdoor) air quality and is directed to review the standards every 5 years. On July 18, 1997, the Agency completed its review of two of the six standards, promulgating a new standard for fine particulates (referred to as PM2.5) and revised standards for ozone and coarse particles (PM10). (For background on the standards, see CRS Report 97-8, Air Quality: Background Analysis of EPA's 1997 Ozone and Particulate Matter Standards.) The net impact of the promulgated standards would be increased stringency. For the new ozone standard, 332 counties have pollutant concentrations above the standard, as compared to 189 counties under the old standard. The new particulate standard is expected to bring at least 100 new counties into nonattainment status, as well. Such an increase in the number of nonattainment areas would have broad implications for the states, affected industries, economic sectors such as agriculture and transportation, and individuals. As a result, Congress has remained interested in the standards and decisions regarding their implementation, and numerous groups have sued EPA to overturn them. On May 14, 1999, the U.S. Court of Appeals for the D.C. Circuit, in a case filed by the American Trucking Associations and other plaintiffs, remanded both the ozone and particulate standards to EPA. In a split decision (2-1), the court ruled that EPA had unconstitutionally usurped legislative powers. In Sections 108 and 109 of the Clean Air Act, Congress directed EPA to establish ambient air quality standards necessary to protect public health with an adequate margin of safety. But the court found that EPA exercised legislative discretion in actually setting the ozone and PM standards, since it was not clear from the statute or from EPA's interpretation of it where the standard should be set. "Although the factors EPA uses in determining the degree of public health concern associated with different levels of ozone and PM are reasonable, EPA appears to have articulated no 'intelligible principle' to channel its application of these factors; nor is one apparent from the statute," according to the opinion. The court also considered several other issues -- rejecting five arguments the plaintiffs made regarding both standards, but finding in favor of the plaintiffs on various issues specific to one or the other standard. Regarding ozone, the court ruled that the 1990 Clean Air Act Amendments preclude EPA from enforcing a revised ozone standard as a result of language in Section 181(a) that requires all nonattainment areas to be classified on the basis of the old 1-hour ozone standard. The court also held that the Agency erred in not considering possible benefits of ground-level ozone in its analysis of the health effects of the pollutant. Regarding particulates, the court concluded that EPA's choice of PM10 as the indicator for coarse particles was arbitrary and capricious. The court concluded that there was "ample support" for the Agency's decision to regulate coarse particles, but argued that the Agency needed to choose an indicator such as PM10-2.5 (particles smaller than 10 microns but larger than 2.5) rather than PM10 (all particles smaller than 10 microns, including fine particles) in its regulations aimed to control the coarse fraction. The 105th Congress conducted a number of oversight hearings on standards-related issues and enacted legislation (P.L. 105-178, Title VI) to address some of the concerns raised. The legislation codified EPA's announced implementation schedule, giving the Agency until July 2000 to designate ozone nonattainment areas and December 2005 to designate PM2.5 areas. Despite remanding the standards to EPA, the Appeals Court left these deadlines for designation of nonattainment areas intact. Designation of areas as nonattainment sets in motion more stringent requirements for permits and a requirement that plans for transportation projects demonstrate that they will "conform" to the area's plan to attain the air quality standard. While these requirements are of concern to the potentially regulated community in those areas likely to be designated nonattainment, the Agency has some discretion in setting the effective date of designations. In a guidance memorandum, EPA stated that, "In the process of determining when to finalize the proposed designations and make them effective, EPA will carefully consider the time needed to prepare for any applicable requirements, as well as the status of ongoing litigation and administrative proceedings." Many in Congress expressed concern, however, that EPA was moving ahead with the designation process, arguing that designation would force state and local governments to dedicate resources toward meeting standards that could be rendered null and void by the courts. On June 21, 2000, Representatives Collins and Linder offered an amendment to the VA-HUD-Independent Agencies Appropriation for FY 2001(H.Amdt. 859 to H.R. 4635) to prohibit EPA from using any funds in the bill prior to June 15, 2001 to designate nonattainment areas under the 8-hour ozone standard. The amendment passed, 225-199. An amendment by Senator Boxer (S.Amdt. 4308), to strike the language from the Senate version of the bill, failed, 63-32, on October 12. The final version of the bill, which was signed into law October 27, 2000 (P.L. 106-377), prohibits designating 8-hour ozone nonattainment areas prior to a Supreme Court decision or June 15, 2001, whichever occurs first. The conferees also agreed to language delaying the application of conformity requirements until one year after an area is designated nonattainment. Meanwhile, the case will proceed to the Supreme Court. After reviewing the appeals court's May 1999 decision, EPA and the Department of Justice decided to appeal the ruling. Since numerous environmental statutes give discretion to the EPA Administrator similar to that termed unconstitutional in this decision, the decision -- if left unchallenged -- could reshape dramatically EPA's authority to promulgate regulations. Acting on EPA's behalf, the Justice Department requested a rehearing by the full (en banc) Court of Appeals; the court rejected that request, October 29, 1999. An appeal to the Supreme Court was accepted on May 22, 2000, however, with oral argument scheduled for November 7. On May 30, the Court also accepted an appeal from the American Trucking Associations and the U.S. Chamber of Commerce, who asked the Court to determine whether EPA must ignore non-health factors, including cost, when it sets National Ambient Air Quality Standards. Oral argument on this appeal also took place November 7. A decision is expected in spring 2001. (For a further discussion of the appeals court ruling, see CRS Report RS20228, The D.C. Circuit Remands the Ozone and Particulate Matter Clean-Air Standards: American Trucking Associations v. EPA, June 10, 1999.) P.L.
106-40, S. 880
(Inhofe) P.L.
106-377, H.R. 4635
(Walsh) H.Con.Res.
256 (Ewing) H.R. 11
(Bilbray) H.R. 25
(Boehlert) H.R. 236
(Rogan) H.R. 657
(Sweeney) H.R. 1367
(Franks) H.R. 1398
(Pombo) H.R. 1626
(Baker) H.R. 1705
(Pallone) H.R. 1790
(Bliley) H.R. 1876
(Talent) H.R. 2427
(Cox) H.R. 2667
(Allen) H.R. 2900
(Waxman) H.R. 2980
(Allen) H.R. 3298
(Barr) H.R. 3326
(Nadler) H.R. 3449
(Greenwood) H.R. 3583
(Linder) H.R. 3686
(Lewis) H.R. 3798
(Forbes) H.R. 4011
(Ganske) H.R. 4120
(Shadegg) H.R. 4215
(Pombo) H.R. 4303
(Ewing) H.R. 4739
(Kucinich) H.R. 4859
(Taylor) S. 172
(Moynihan) S. 266
(Feinstein) S. 268
(Feinstein) S. 495 (Bond)
S. 645
(Feinstein) S. 673
(Leahy) S. 1037
(Boxer) S. 1053
(Bond) S. 1731
(Chafee) S. 1886
(Inhofe) S. 1949
(Leahy) S. 2088
(Cleland) S. 2233
(Fitzgerald) S. 2362
(Voinovich) S. 2503
(Daschle) S. 2504
(Craig) S. 2546
(Bond) S. 2723
(Inhofe) S. 2962 (B.
Smith) S. 2971
(Harkin) CONGRESSIONAL HEARINGS, REPORTS, AND DOCUMENTS U.S. Congress. House. Committee on Commerce. Subcommittee on Health and Environment. National Implementation of the Reformulated Gasoline (RFG) Program. March 2, 2000. U.S. Congress. Senate. Committee on Environment and Public Works. Conformity Regulations. July 14, 1999. U.S. Congress. Senate. Committee on Environment and Public Works. Subcommittee on Clean Air, Wetlands, Private Property, and Nuclear Safety. Clean Air Act Reauthorization. October 14, 1999 and September 27, 2000. -----. Environmental Benefits and Impacts of Ethanol Under the Clean Air Act. June 14, 2000. -----. Highway Diesel Sulfur Regulations. June 15 and September 21, 2000. CRS Issue Brief IB97003. Stratospheric Ozone Depletion: Implementation Issues, by Larry B. Parker. (Updated regularly) CRS Report 98-236. Air Quality: EPA's Ozone Transport Rule, OTAG, and Section 126 Petitions -- A Hazy Situation?, by Larry Parker and John Blodgett. Updated March 10, 2000. 24 p. CRS Report RL30298. Air Quality and Motor Vehicles: An Analysis of Current and Proposed Emission Standards, by David M. Bearden. September 2, 1999. 21 p. CRS Report RS20459 . Diesel Fuel and Engines: An Overview of New Emissions Regulations, by Brent D. Yacobucci. Updated October 3, 2000. 6 p. CRS Report RL30131 . Highway Fund Sanctions and Conformity Under the Clean Air Act, by James E. McCarthy. Updated October 15, 1999. 8 p. CRS Report 98-290. MTBE in Gasoline: Clean Air and Drinking Water Issues, by James E. McCarthy and Mary Tiemann. Updated October 2, 2000. 23 p. CRS Report 96-737. Nitrogen Oxides and Electric Utilities: Revising the NSPS, by Larry Parker. Updated October 13, 1998. 6 p. CRS Report RS20228 , The D.C. Circuit Remands the Ozone and Particulate Matter Clean-Air Standards: American Trucking Associations v. EPA, by Robert Meltz and James E. McCarthy. June 10, 1999. 6 p. |
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