Claudia Copeland
Specialist in Resources and Environmental Policy
Mountaintop removal mining involves removing the top of a mountain in order to recover the coal seams contained there. This practice occurs in six Appalachian states (Kentucky, West Virginia, Virginia, Tennessee, Pennsylvania, and Ohio). It creates an immense quantity of excess spoil (dirt and rock that previously composed the mountaintop), which is typically placed in valley fills on the sides of the former mountains, burying streams that flow through the valleys. Critics say that, as a result of valley fills, stream water quality and the aquatic and wildlife habitat that streams support are destroyed by tons of rocks and dirt. The mining industry argues that mountaintop mining is essential to conducting surface coal mining in the Appalachian region and that surface coal mining would not be economically feasible there if producers were restricted from using valleys for the disposal of mining overburden.
Mountaintop mining is regulated under several laws, including the Clean Water Act (CWA) and the Surface Mining Control and Reclamation Act (SMCRA). In June 2009, officials of the Environmental Protection Agency (EPA), the U.S. Army Corps of Engineers (Corps), and the Department of the Interior signed a Memorandum of Understanding outlining a series of administrative actions under these laws to reduce the harmful environmental impacts of mountaintop mining and surface coal mining in Appalachia. The plan includes a series of nearterm and longer-term actions that emphasize specific steps, improved coordination, and greater transparency of decisions. The actions are being implemented through regulatory proposals, guidance documents, and review of pending applications for permits to authorize surface coal mining operations in Appalachia. This report provides background on regulatory requirements, controversies and legal challenges to mountaintop mining, and recent actions and proposals by the Administration.
Congressional interest in these issues also is discussed, including legislation in the 111th Congress that sought to restrict the practice of mountaintop mining (H.R. 1310 and S. 696) and other legislation that sought to block the Administration’s regulatory actions (H.R. 6113/S. 3933). Controversy has been generated by EPA’s January 2011 veto of a CWA permit for a surface coal mining project in West Virginia, and attention by the 112th Congress to the veto and other EPA actions is likely.
Date of Report: January 25, 2011
Number of Pages: 17
Order Number: RS21421
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Robert Esworthy
Specialist in Environmental Policy
James E. McCarthy
Specialist in Environmental Policy
Following its review of more than 2,000 scientific studies, on October 17, 2006, the Environmental Protection Agency (EPA) published its final revisions to the National Ambient Air Quality Standards (NAAQS) for particulate matter (particulates, or PM). Several states and industry, agriculture, business, and environmental and public health advocacy groups petitioned the court, challenging certain aspects of EPA’s revisions. A February 24, 2009, decision by the U.S. Court of Appeals for the District of Columbia Circuit granted the petitions in part, denying other challenges, and remanded the standards to EPA for further consideration. While the court did not specifically vacate the 2006 PM standards, EPA has announced its intention to accelerate its ongoing next round of the periodic review of the particulates NAAQS, in part, in response to the court’s decision. These actions, and EPA’s ongoing implementation of the 2006 PM NAAQS, have prompted renewed interest among members of Congress.
Experiences and issues leading up to and following the promulgation of the 2006 PM2.5 NAAQS could provide relevant insights as EPA proceeds with its current review of the particulates NAAQS. Although a tightening of the standards, the 2006 particulates NAAQS are not as stringent as recommended by EPA staff or the independent scientific advisory committee mandated under the Clean Air Act (Clean Air Scientific Advisory Committee, or CASAC). The divergence from the CASAC’s recommendations proved controversial, as did several other elements of the 2006 particulates NAAQS, including the decision not to exclude rural sources from the coarse particle standard. Some have also questioned the EPA’s strengthening of the standard for all fine particles, without distinguishing their source or chemical composition.
The EPA found that the evidence continued to support associations between exposure to particulates in ambient air and numerous significant health problems. Based on several analytical approaches, the EPA estimated that compliance with the revised NAAQS will prevent 1,200 to 13,000 premature deaths annually, as well as substantial numbers of hospital admissions and missed work or school days due to illness. Based on these findings, EPA revised the PM NAAQS by strengthening the preexisting (1997) standard for “fine” particulate matter 2.5 micrometers or less in diameter (PM2.5) by lowering the allowable daily concentration averaged over 24-hour periods of PM2.5 in the air. The annual PM2.5 standard, which is set in addition to the daily standard to address human health effects from chronic exposures to the pollutants, is unchanged from the 1997 standard. The decision not to tighten the annual standard was reversed by the D.C. Circuit and remanded to EPA for consideration.
The 2006 particulates NAAQS also retained the 24-hour standard and revoked the annual standard for slightly larger, but still inhalable, particles less than or equal to 10 micrometers (PM10). The EPA abandoned its proposal to replace the particle size indicator of PM10 with a range of 10 to 2.5 micrometers (PM10-2.5). The D.C. Circuit’s February 24, 2009, decision upheld EPA’s decisions with regard to PM10 NAAQS.
EPA’s ongoing implementation of the 2006 NAAQS, including EPA’s November 13, 2009, final designation of those geographical areas not in compliance (typically defined by counties or portions of counties), has been an area of debate among some members of Congress, states, and other stakeholders. Although EPA is not requiring new nonattainment designations for PM10, the tightening of the PM2.5 standard increased the number of areas in nonattainment. EPA’s final designations for the 2006 PM NAAQS include 120 counties and portions of counties in 18 states as nonattainment areas based on 2006 through 2008 air quality monitoring data.
Date of Report: January 13, 2011
Number of Pages: 29
Order Number: RL34762
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Linda Luther
Analyst in Environmental Policy
Beginning in the late 1950s and through the 1960s, Congress reacted to increasing public concern about the impact that human activity could have on the environment. A key legislative option to address this concern was the declaration of a national environmental policy. Advocates of this approach argued that without a specific policy, federal agencies were neither able nor inclined to consider the environmental impacts of their actions in fulfilling the agency’s mission. The statute that ultimately addressed this issue was the National Environmental Policy Act of 1969 (NEPA, 42 U.S.C. §§ 4321-4347).
Signed into law by President Nixon on January 1, 1970, NEPA was the first of several major environmental laws passed in the 1970s. It declared a national policy to protect the environment and created a Council on Environmental Quality (CEQ) in the Executive Office of the President. To implement the national policy, NEPA required that a detailed statement of environmental impacts be prepared for all major federal actions significantly affecting the environment. The “detailed statement” would ultimately be referred to as an environmental impact statement (EIS).
With an initial absence of regulations specifying implementation procedures and no agency authorized to enforce the law, federal agencies reacted in different ways to NEPA’s requirements. Some had difficulty complying with the law’s EIS requirements. As a result, litigation that served to interpret NEPA’s requirements and enforce agency compliance began almost immediately. In addition to questions of procedure (e.g., how, when, or why an EIS must be prepared), another question was how the environmental policy goals of the act should be implemented or enforced. The courts ultimately decided that NEPA is a procedural statute with twin aims requiring agencies to (1) consider the environmental impacts of their proposed actions and (2) inform the public that they (the agencies) considered environmental concerns in their decision-making process. In that capacity, NEPA has become a primary mechanism for public participation in the federal decisionmaking process.
As it has been implemented, most agencies use NEPA as an “umbrella” statute. As such, NEPA forms a framework to coordinate or demonstrate compliance with any study, review, or consultation required by other environmental laws. The use of NEPA in this capacity can lead to confusion. The need to comply with another environmental law, such as the Clean Water Act, may be identified within the framework of the NEPA process, but NEPA itself is not the source of the obligation. Theoretically, if the requirement to comply with NEPA were removed, compliance with each applicable law would still be required.
Date of Report: January 10, 2011
Number of Pages: 36
Order Number: RL33152
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Claudia Copeland
Specialist in Resources and Environmental Policy
From an environmental quality standpoint, much of the public and policy interest in animal agriculture has focused on impacts on water resources, because animal waste, if not properly managed, can harm water quality through surface runoff, direct discharges, spills, and leaching into soil and groundwater. A more recent issue is the contribution of air emissions from animal feeding operations (AFOs), enterprises where animals are raised in confinement. This report provides background on the latter issue.
AFOs can affect air quality through emissions of gases such as ammonia and hydrogen sulfide, particulate matter, volatile organic compounds, hazardous air pollutants, and odor. These pollutants and compounds have a number of environmental and human health effects.
Agricultural operations have been treated differently from other businesses under numerous federal and state laws. Some environmental laws specifically exempt agriculture from regulatory provisions, and some are designed so that farms are not subject to most, if not all, of the regulatory impact. The primary regulatory focus on environmental impacts has occurred under the Clean Water Act. In addition, AFOs that emit large quantities of air pollutants may be subject to Clean Air Act regulation. Some livestock operations also may be regulated under the release reporting requirements of the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) and the Emergency Planning and Community Right-to-Know Act (EPCRA). Questions about the applicability of these laws to livestock and poultry operations have been controversial and have drawn congressional attention. Agriculture’s role as both a source of and a “sink” for greenhouse gases also has been of interest recently in connection with addressing the global challenge of climate change.
Enforcement of environmental laws requires accurate measurement of emissions to determine whether regulated pollutants are emitted in quantities that exceed specified thresholds. Two reports by the National Research Council evaluated the current state of the science and approaches for estimating AFO air emissions to guide future management and regulatory efforts. In an effort to collect scientifically credible data on air emissions, in January 2005 the Environmental Protection Agency (EPA) announced a plan negotiated with segments of the animal agriculture industry. Called the Air Compliance Agreement, it is intended to produce air quality monitoring data on AFO emissions, while at the same time protecting participants through a “safe harbor” from liability under certain provisions of federal environmental laws. Issues related to this agreement, which has been controversial among environmental advocates, state and local air quality officials, and some industry groups, are discussed separately in CRS Report RL32947, Air Quality Issues and Animal Agriculture: EPA’s Air Compliance Agreement.
Results of the 2010 congressional elections have altered political dynamics in Congress on many issues, and different approaches are anticipated in the 112th Congress. Many stakeholders anticipate that through oversight or legislative proposals, the 112th Congress will be interested in examining how EPA’s activities, including many discussed in this report, may affect agriculture.
Date of Report: January 19, 2011
Number of Pages: 34
Order Number: RL32948
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Claudia Copeland
Specialist in Resources and Environmental Policy
From an environmental quality standpoint, much of the interest in animal agriculture has focused on impacts on water resources, because animal waste, if not properly managed, can harm water quality through surface runoff, direct discharges, spills, and leaching into soil and groundwater. A more recent issue is the contribution of emissions from animal feeding operations (AFO), enterprises where animals are raised in confinement, to air pollution. AFOs can affect air quality through emissions of gases such as ammonia and hydrogen sulfide, particulate matter, volatile organic compounds, hazardous air pollutants, and odor. These pollutants and compounds have a number of environmental and human health effects.
Agricultural operations that emit large quantities of air pollutants may be subject to Clean Air Act (CAA) regulation and permits. Further, some livestock operations also may be regulated under the release reporting requirements of the Comprehensive Environmental Response, Compensation, and Liability Act (Superfund, or CERCLA) and the Emergency Planning and Community Right-to-Know Act (EPCRA). Questions about the applicability of these laws to livestock and poultry operations have been controversial and have drawn congressional attention.
Enforcement of these federal environmental laws requires accurate measurement of emissions to determine whether regulated pollutants are emitted in quantities that exceed specified thresholds. Yet experts believe that existing data provide a poor basis for regulating and managing air emissions from AFOs. In an effort to collect scientifically credible data, in 2005 the Environmental Protection Agency (EPA) announced a plan that had been negotiated with segments of the animal agriculture industry. Called the Air Compliance Agreement, it is intended to produce air quality monitoring data on AFO emissions during a two-year study, while at the same time protecting participants through a “safe harbor” from liability under certain provisions of federal environmental laws. Many producer groups supported the agreement as essential to gathering valid data that are needed for decision making. However, critics, including environmentalists and state and local air quality officials, said that the Air Compliance Agreement would grant all participating animal producers a sweeping retrospective and prospective liability shield for violations of environmental laws, yet because fewer than 30 farms would be monitored, it was too limited in scope to yield scientifically credible estimates of AFO emissions. Some industry groups had their own questions and reservations. In August 2006, EPA approved agreements with 2,568 AFOs, representing more than 13,000 farms. Monitoring, involving 24 farms in 9 states, occurred from mid-2007 to the end of 2009. In January 2011, EPA released the data from the individual monitored sites. The agency will use the emissions data to develop improved emissions estimating methodologies.
Separately from the monitoring study, in December 2008, EPA issued a rule to exempt animal waste emissions to the air from most CERCLA and EPCRA reporting requirements. Legal challenges to the rule followed. In October 2010, a federal court approved the government’s request to remand the rule to EPA for reconsideration and possible modification.
This report reviews key issues associated with the Air Compliance Agreement. Background information on air emissions from poultry and livestock operations, relevant federal environmental laws and regulations, congressional interest, state activities, and research needs are discussed in CRS Report RL32948, Air Quality Issues and Animal Agriculture: A Primer, by Claudia Copeland.
Date of Report: January 18, 2011
Number of Pages: 16
Order Number: RL32947
Price: $29.95
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