Congressional Research Service Report Released: Controlling Air Emissions from Outer Continental Shelf Sources: A Comparison of Two Programs—EPA and DOI
The Congressional Research Service (CRS), the public policy research arm of Congress, just issued the report Controlling Air Emissions from Outer Continental Shelf Sources: A Comparisonof Two Programs—EPA and DOI (Nov. 26, 2012). The 33-page report authored by Jonathan L. Ramseur discusses the following:
Air emissions
from outer continental shelf (OCS) operations are subject to different
regulatory programs, depending on the location of the operation. The Department
of the Interior (DOI) has jurisdiction over OCS sources in federal waters in
the western Gulf of Mexico and most of the central Gulf. In addition, the
Consolidated Appropriations Act, 2012 (P.L. 112-74), transferred air emission
authority in the OCS off Alaska’s north coast from the Environmental Protection
Agency (EPA) to DOI. EPA has jurisdiction over sources in all other federal
waters.
The primary
difference between the EPA and DOI programs is rooted in the different
statutory authorities: the 1990 Clean Air Act (CAA) and the 1978 Outer
Continental Shelf Lands Act (OCSLA). The primary objectives of these statutes
are different—air quality versus offshore energy development. The two
regulatory programs reflect these underlying differences. For much of the past
30 years, these differences received little attention, primarily because most
of the federal oil and gas resources in EPA’s jurisdiction have been subject to
moratoria. In 2008, moratoria provisions expired, potentially opening many of
the areas in EPA’s jurisdiction to oil and gas leasing activity. If more OCS
areas in EPA’s jurisdiction are open for oil and gas leasing, policymakers
interest in these differences will likely increase.
For OCS
sources in EPA’s jurisdiction, requirements depend on whether the source is
located within 25 miles of a state’s seaward boundary (“inner OCS sources”) or
beyond (“outer OCS sources”). Inner OCS sources are subject to the same requirements
as comparable onshore emission sources, which vary by state and depend on the
area’s air quality status; outer sources are subject to various CAA provisions,
including the Prevention of Significant Deterioration (PSD) program. In
contrast, OCS sources in DOI’s jurisdiction are subject to air emission requirements
only if emissions would “significantly affect” onshore air quality.
A key
difference between the EPA and DOI programs is the federal emission threshold
that would subject a source to substantive requirements. For sources in EPA’s
jurisdiction, this is the PSD threshold of 250 tons per year (tpy) of regulated
emissions. Sources that exceed this level would likely be subject to Best
Achievable Control Technology (BACT) and other provisions. States’ analogous
thresholds that apply to inner OCS sources may be more stringent. By
comparison, a DOI OCS source applies an exemption formula, based on distance
from shore (e.g., a source 30 miles from shore would have an emission threshold
of 990 tpy). If a source remains subject after this step, it must conduct air
modeling to assess whether its emissions would have a significant effect on
onshore air quality. In effect, this two-step process constitutes a much less
stringent threshold than EPA’s 250 tpy threshold.
Another
substantial difference is the time frame allotted to the agencies for reviewing
a potential source’s permit (EPA) or activity-specific plan (DOI). In addition,
the EPA permit process allows greater opportunity for input from the public. In
particular, EPA’s Environmental Appeals Board offers parties a powerful tool to
compel agency review.
Therefore, two
identical operations, located in separate jurisdictions, could face
considerably different requirements and procedural time frames. Some stakeholders
would likely argue that the additional opportunities for public involvement in
EPA’s permit process help create a balance between resource development and
environmental concerns. Others would likely contend these steps present
unnecessary burdens and timing uncertainty in the process.
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