[Federal Register Volume 64, Number 241 (Thursday, December 16, 1999)]
[Proposed Rules]
[Pages 70319-70332]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 99-31709]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[MA069-7205:FRL-6501-8]
Approval and Promulgation of Implementation Plans; Massachusetts;
One-Hour Ozone Attainment Demonstration for the Springfield (Western
Massachusetts) Ozone Nonattainment Area
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
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SUMMARY: The EPA is proposing to approve the ground-level one-hour
ozone attainment demonstration State Implementation Plan (SIP) for the
Springfield (Western Massachusetts) ozone nonattainment area submitted
by the then Commissioner of the Massachusetts Department of
Environmental Protection (MA DEP) on July 27, 1998. We are also
proposing to approve an attainment date extension for this area to
December 31, 2003, which was requested by the current MA DEP
Commissioner on August 13, 1999. We are also proposing, in the
alternative, to disapprove this demonstration if Massachusetts does not
submit: Revisions to the Massachusetts stage II vapor recovery rule
that were committed to in the July 27, 1998 attainment demonstration;
and the demonstration described in EPA's supplementary proposed
approval of the Massachusetts 15% rate-of-progress plan published in
the Federal Register on November 30, 1999, requiring Massachusetts to
demonstrate that the emission reduction credit it is claiming for its
I/M program in the Western Massachusetts attainment demonstration is
warranted for the combination of test type and equipment that
Massachusetts is implementing.
DATES: Comments must be received on or before February 14, 2000.
ADDRESSES: Written comments (in duplicate if possible) should be sent
to: David B. Conroy at the EPA Region I (New England) Office, One
Congress Street, Suite 1100-CAQ, Boston, Massachusetts 02114-2023.
Copies of the State submittal and EPA's technical support document
are available for public inspection during normal business hours (9
a.m. to 4 p.m.) at the following addresses: U.S. Environmental
Protection Agency, Region 1 (New England), One Congress St., 11th
Floor, Boston, Massachusetts, telephone (617) 918-1664, and at the
Division of Air Quality Control, Department of Environmental
Protection, One Winter Street, 8th Floor, Boston, Massachusetts 02108.
Please telephone in advance before visiting.
FOR FURTHER INFORMATION CONTACT: Richard Burkhart, (617) 918-1664.
SUPPLEMENTARY INFORMATION: This document provides background
information on attainment demonstration SIPs for the one-hour ozone
national ambient air quality standard (NAAQS) and an analysis of the
one-hour ozone attainment demonstration SIP submitted by the MA DEP for
the Western Massachusetts ozone nonattainment area. This document
addresses the following questions:
What is the Basis for the Attainment Demonstration SIP?
What are the Components of a Modeled Attainment Demonstration?
What is the Frame Work for Proposing Action on the Attainment
Demonstration SIPs?
What Does EPA Expect to Happen with Respect to the Attainment
Demonstration for the Springfield (Western Massachusetts) One-hour
Ozone Nonattainment Area?
What are the Relevant Policy and Guidance Documents?
How Does the Massachusetts Submittal Satisfy the Frame Work?
I. Background Information
A. What Is the Basis for the State's Attainment Demonstration SIP?
1. CAA Requirements
The Clean Air Act (CAA) requires EPA to establish national ambient
air quality standards (NAAQS or standards) for certain widespread
pollutants that cause or contribute to air pollution that is reasonably
anticipated to endanger public health or welfare. CAA sections 108 and
109. In 1979, EPA promulgated the one-hour 0.12 parts per million (ppm)
ground-level ozone standard. 44 FR 8202 (Feb. 8, 1979). Ground-level
ozone is not emitted directly by sources. Rather, emissions of nitrogen
oxides (NOX) and volatile organic compounds (VOCs) react in
the presence of sunlight to form ground-level ozone. NOX and
VOC are referred to as precursors of ozone.
An area exceeds the one-hour ozone standard each time an ambient
air quality monitor records a one-hour average ozone concentration
above 0.124 ppm. An area is violating the standard if, over a
consecutive three-year period, more than three exceedances are expected
to occur at any one monitor. The CAA, as amended in 1990, required EPA
to designate as nonattainment any area that was violating the one-hour
ozone standard,
[[Page 70320]]
generally based on air quality monitoring data from the three-year
period from 1987-1989. CAA section 107(d)(4); 56 FR 56694 (Nov. 6,
1991). The CAA further classified these areas, based on the area's
design value, as marginal, moderate, serious, severe or extreme. CAA
section 181(a). Marginal areas were suffering the least significant air
pollution problems while the areas classified as severe and extreme had
the most significant air pollution problems.
The control requirements and dates by which attainment needs to be
achieved vary with the area's classification. Marginal areas are
subject to the fewest mandated control requirements and have the
earliest attainment date. Severe and extreme areas are subject to more
stringent planning requirements but are provided more time to attain
the standard. Serious areas are required to attain the one-hour
standard by November 15, 1999 and severe areas are required to attain
by November 15, 2005 or November 15, 2007. The Western Massachusetts
area is classified as serious and its attainment date is November 15,
1999.
Under section 182(c)(2) and (d) of the CAA, serious and severe
areas were required to submit by November 15, 1994 demonstrations of
how they would attain the one-hour standard and how they would achieve
reductions in VOC emissions of 9 percent for each three-year period
until the attainment year (rate-of-progress or ROP). (In some cases,
NOX emission reductions can be substituted for the required
VOC emission reductions.) Today, in this proposed rule, EPA is
proposing action on the attainment demonstration SIP submitted by the
MA DEP for the Western Massachusetts nonattainment area. EPA has
already proposed approval of the State's 9% ROP for the Western
Massachusetts area (64 FR 51943; September 27, 1999 and 64 FR 66829,
November 30, 1999). In addition, elsewhere in this Federal Register,
EPA is today proposing to take action on nine other serious or severe
one-hour ozone attainment demonstrations and, in some cases, ROP SIPs.
The additional nine areas are, Greater Connecticut, New York-North New
Jersey-Long Island (NY-NJ-CT), Baltimore (MD), Philadelphia-Wilmington-
Trenton (PA-NJ-DE-MD), Metropolitan Washington, D.C. (DC-MD-VA),
Atlanta (GA), Milwaukee-Racine (WI), Chicago-Gary-Lake County (IL-IN),
and Houston-Galveston-Brazoria (TX).
In general, an attainment demonstration SIP includes a modeling
analysis component showing how the area will achieve the standard by
its attainment date and the control measures necessary to achieve those
reductions. Another component of the attainment demonstration SIP is a
motor vehicle emissions budget for transportation conformity purposes.
Transportation conformity is a process for ensuring that States
consider the effects of emissions associated with new or improved
federally-funded roadways on attainment of the standard. As described
in section 176(c)(2)(A) of the CAA, attainment demonstrations
necessarily include the estimates of motor vehicle emissions that are
consistent with attainment, which then act as a budget or ceiling for
the purposes of determining whether transportation plans and projects
conform to the attainment SIP.
2. History and Time Frame for the State's Attainment Demonstration SIP
Notwithstanding significant efforts by the States, in 1995 EPA
recognized that many States in the eastern half of the United States
could not meet the November 1994 time frame for submitting an
attainment demonstration SIP because emissions of NOX and
VOCs in upwind States (and the ozone formed by these emissions)
affected these nonattainment areas and the full impact of this effect
had not yet been determined. This phenomenon is called ozone transport.
On March 2, 1995, Mary D. Nichols, EPA's then Assistant
Administrator for Air and Radiation, issued a memorandum to EPA's
Regional Administrators acknowledging the efforts made by States but
noting the remaining difficulties in making attainment demonstration
SIP submittals.1 Recognizing the problems created by ozone
transport, the March 2, 1995 memorandum called for a collaborative
process among the States in the eastern half of the country to evaluate
and address transport of ozone and its precursors. This memorandum led
to the formation of the Ozone Transport Assessment Group (OTAG)
2 and provided for the States to submit the attainment
demonstration SIPs based on the expected time frames for OTAG to
complete its evaluation of ozone transport.
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\1\ Memorandum, ``Ozone Attainment Demonstrations,'' issued
March 2, 1995. A copy of the memorandum may be found on EPA's web
site at http://www.epa.gov/ttn/oarpg/t1pgm.html.
\2\ Letter from Mary A. Gade, Director, State of Illinois
Environmental Protection Agency to Environmental Council of States
(ECOS) Members, dated April 13, 1995.
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In June 1997, OTAG concluded and provided EPA with recommendations
regarding ozone transport. The OTAG generally concluded that transport
of ozone and the precursor NOX is significant and should be
reduced regionally to enable States in the eastern half of the country
to attain the ozone NAAQS.
In recognition of the length of the OTAG process, in a December 29,
1997 memorandum, Richard Wilson, EPA's then Acting Assistant
Administrator for Air and Radiation, provided until April 1998 for
States to submit the following elements of their attainment
demonstration SIPs for serious and severe nonattainment areas: (1)
Evidence that the applicable control measures in subpart 2 of part D of
title I of the CAA were adopted and implemented or were on an
expeditious course to being adopted and implemented; (2) a list of
measures needed to meet the remaining ROP emissions reduction
requirement and to reach attainment; (3) for severe areas only, a
commitment to adopt and submit target calculations for post-1999 ROP
and the control measures necessary for attainment and ROP plans through
the attainment year by the end of 2000; (4) a commitment to implement
the SIP control programs in a timely manner and to meet ROP emissions
reductions and attainment; and (5) evidence of a public hearing on the
State submittal.3 This submission is sometimes referred to
as the Phase 2 submission. Motor vehicle emissions budgets can be
established based on a commitment to adopt the measures needed for
attainment and identification of the measures needed. Thus, State
submissions due in April 1998 under the Wilson policy should have
included a motor vehicle emissions budget.
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\3\ Memorandum, ``Guidance for Implementing the 1-Hour Ozone and
Pre-Existing PM 10 NAAQS,'' issued December 29, 1997. A copy of this
memorandum may be found on EPA's web site at http://www.epa.gov/ttn/
oarpg/t1pgm.html.
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Building upon the OTAG recommendations and technical analyses, in
November 1997, EPA proposed action addressing the ozone transport
problem. In its proposal, the EPA found that current SIPs in 22 States
and the District of Columbia (23 jurisdictions) were insufficient to
provide for attainment and maintenance of the one-hour standard because
they did not regulate NOX emissions that significantly
contribute to ozone transport. 62 FR 60318 (Nov. 7, 1997). The EPA
finalized that rule in September 1998, calling on the 23 jurisdictions
to revise their SIPs to require NOX emissions reductions
within the State to a level consistent with a NOX emissions
budget identified in the final rule. 63 FR 57356 (Oct. 27,
[[Page 70321]]
1998). This final rule is commonly referred to as the NOX
SIP Call.
3. Attainment Date Delays Due to Transport
On July 16, 1998, EPA's then Acting Assistant Administrator,
Richard Wilson, issued a guidance memorandum intended to provide
further relief to areas affected by ozone transport.4 The
memorandum recognized that many moderate and serious areas are affected
by transported pollution from either an upwind area in the same State
with a higher classification and later attainment date, and/or from an
upwind area in another State that is significantly contributing to the
downwind area's nonattainment problem. The policy recognized that some
downwind areas may be unable to meet their own attainment dates,
despite doing all that was required in their local area, because an
upwind area may not have adopted and implemented all of the controls
that would benefit the downwind area through control of transported
ozone before the downwind area's attainment date. Thus, the policy
provided that upon a successful demonstration that an upwind area has
interfered with attainment and that the downwind area is adopting all
measures required for its local area 5 for attainment but
for this interference, EPA may grant an extension of the downwind
area's attainment date.6 Once an area receives an extension
of its attainment date based on transport, the area would no longer be
subject to reclassification to a higher classification and subject to
additional requirements for failure to attain by its original
attainment date provided it was doing all that was necessary locally.
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\4\ Memorandum, ``Extension of Attainment Dates for Downwind
Transport Areas,'' issued July 16, 1998. This memorandum is
applicable to both moderate and serious ozone nonattainment areas. A
copy of this policy may be found on EPA's web site at http://
www.epa.gov/ttn/oarpg/t1pgm.html.
\5\ Local area measures would include all of the measures within
the local modeling domain that were relied on for purposes of the
modeled attainment demonstration.
\6\ The policy provides that the area must meet four criteria to
receive an attainment date extension. In summary, the area must: (1)
Be identified as a downwind area affected by transport from either
an upwind area in the same State with a later attainment date or an
upwind area in another State that significantly contributes to
downwind nonattainment; (2) submit an approvable attainment
demonstration with any necessary, adopted local measures and with an
attainment date that reflects when the upwind reductions will occur;
(3) adopt all local measures required under the area's current
classification and any additional measures necessary to demonstrate
attainment; and (4) provide that it will implement all adopted
measures as expeditiously as practicable, but no later than the date
by which the upwind reductions needed for attainment will be
achieved.
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A request from the MA DEP for such an extension of the attainment
date for the Western Massachusetts nonattainment area and EPA's
proposed response is discussed in this action.
4. Time Frame for Taking Action on Attainment Demonstration SIPs for 10
Serious and Severe Areas
The States generally submitted the SIPs between April and October
of 1998; some States are still submitting additional revisions as
described below. Under the CAA, EPA is required to approve or
disapprove a State's submission no later than 18 months following
submission. (The statute provides up to 6 months for a completeness
determination and an additional 12 months for approval or disapproval.)
The EPA believes that it is important to keep the process moving
forward in evaluating these plans and, as appropriate, approving them.
Thus, in today's Federal Register, EPA is proposing to take action on
the 10 serious and severe one-hour ozone attainment demonstration SIPs
(located in 13 States and the District of Columbia) and intends to take
final action on these submissions over the next 6-12 months. The reader
is referred to individual dates in this document for specific
information on actions leading to EPA's final rulemaking on these
plans.
5. Options for Action on a State's Attainment Demonstration SIP
Depending on the circumstances unique to each of the 10 area SIP
submissions on which EPA is proposing action today, EPA is proposing
one or more of these types of approval or disapproval in the
alternative. In addition, these proposals may identify additional
action that will be necessary from the State.
The CAA provides for EPA to approve, disapprove, partially approve
or conditionally approve a State's plan submission. CAA section 110(k).
The EPA must fully approve the submission if it meets the attainment
demonstration requirement of the CAA. If the submission is deficient in
some way, EPA may disapprove the submission. In the alternative, if
portions of the submission are approvable, EPA may partially approve
and partially disapprove, or may conditionally approve based on a
commitment to correct the deficiency by a date certain, which can be no
later than one year from the date of EPA's final conditional approval.
The EPA may partially approve a submission if separable parts of
the submission, standing alone, are consistent with the CAA. For
example, if a State submits a modeled attainment demonstration,
including control measures, but the modeling does not demonstrate
attainment, EPA could approve the control measures and disapprove the
modeling for failing to demonstrate attainment.
EPA may issue a conditional approval based on a State's commitment
to expeditiously correct a deficiency by a date certain that can be no
later than one year following EPA's conditional approval. Such
commitments do not need to be independently enforceable because, if the
State does not fulfill its commitment, the conditional approval is
converted to a disapproval. For example, if a State commits to submit
additional control measures and fails to submit them or EPA determines
the State's submission of the control measures is incomplete, the EPA
will notify the State by letter that the conditional approval has been
converted to a disapproval. If the State submits control measures that
EPA determines are complete or that are deemed complete, EPA will
determine through rulemaking whether the State's attainment
demonstration is fully approvable or whether the conditional approval
of the attainment demonstration should be converted to a disapproval.
Finally, EPA has recognized that in some limited circumstances, it
may be appropriate to issue a full approval for a submission that
consists, in part, of an enforceable commitment. Unlike the commitment
for conditional approval, such an enforceable commitment can be
enforced in court by EPA or citizens. In addition, this type of
commitment may extend beyond one year following EPA's approval action.
Thus, EPA may accept such an enforceable commitment where it is
infeasible for the State to accomplish the necessary action in the
short term.
B. What Are the Components of a Modeled Attainment Demonstration?
The EPA provides that States may rely on a modeled attainment
demonstration supplemented with additional evidence to demonstrate
attainment. In order to have a complete modeling demonstration
submission, States should have submitted the required modeling analysis
and identified any additional evidence that EPA should consider in
evaluating whether the area will attain the standard.
[[Page 70322]]
1. Modeling Requirements
For purposes of demonstrating attainment, the CAA requires serious
and severe areas to use photochemical grid modeling or an analytical
method EPA determines to be as effective.7 The photochemical
grid model is set up using meteorological conditions conducive to the
formation of ozone. Emissions for a base year are used to evaluate the
model's ability to reproduce actual monitored air quality values and to
predict air quality changes in the attainment year due to the emission
changes which include growth up to and controls implemented by the
attainment year. A modeling domain is chosen that encompasses the
nonattainment area. Attainment is demonstrated when all predicted
concentrations inside the modeling domain are at or below the NAAQS or
at an acceptable upper limit above the NAAQS permitted under certain
conditions by EPA's guidance. When the predicted concentrations are
above the NAAQS, an optional Weight Of Evidence (WOE) determination
which incorporates, but is not limited to, other analyses, such as air
quality and emissions trends, may be used to address uncertainty
inherent in the application of photochemical grid models.
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\7\ The EPA issued guidance on the air quality modeling that is
used to demonstrate attainment with the one-hour ozone NAAQS. See
U.S. EPA, (1991), Guideline for Regulatory Application of the Urban
Airshed Model, EPA-450/4-91-013, (July 1991). A copy may be found on
EPA's web site at http://www.epa.gov/ttn/scram/ (file name:
``UAMREG''). See also U.S. EPA, (1996), Guidance on Use of Modeled
Results to Demonstrate Attainment of the Ozone NAAQS, EPA-454/B-95-
007, (June 1996). A copy may be found on EPA's web site at http://
www.epa.gov/ttn/scram/ (file name: ``O3TEST'').
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The EPA guidance identifies the features of a modeling analysis
that are essential to obtain credible results. First, the State must
develop and implement a modeling protocol. The modeling protocol
describes the methods and procedures to be used in conducting the
modeling analyses and provides for policy oversight and technical
review by individuals responsible for developing or assessing the
attainment demonstration (State and local agencies, EPA Regional
offices, the regulated community, and public interest groups). Second,
for purposes of developing the information to put into the model, the
State must select air pollution days, i.e., days in the past with bad
air quality, that are representative of the ozone pollution problem for
the nonattainment area. Third, the State needs to identify the
appropriate dimensions of the area to be modeled, i.e., the domain
size. The domain should be larger than the designated nonattainment
area to reduce uncertainty in the boundary conditions and should
include large upwind sources just outside the nonattainment area. In
general, the domain is considered the local area where control measures
are most beneficial to bring the area into attainment. Fourth, the
State needs to determine the grid resolution. The horizontal and
vertical resolutions in the model affect the dispersion and transport
of emission plumes. Artificially large grid cells (too few vertical
layers and horizontal grids) may dilute concentrations and may not
properly consider impacts of complex terrain, complex meteorology, and
land/water interfaces. Fifth, the State needs to generate
meteorological data that describe atmospheric conditions and emissions
inputs. Finally, the State needs to verify that the model is properly
simulating the chemistry and atmospheric conditions through diagnostic
analyses and model performance tests. Once these steps are
satisfactorily completed, the model is ready to be used to generate air
quality estimates to support an attainment demonstration.
The modeled attainment test compares model-predicted one-hour daily
maximum concentrations in all grid cells for the attainment year to the
level of the NAAQS. A predicted concentration above 0.124 ppm ozone
indicates that the area is expected to exceed the standard in the
attainment year and a prediction at or below 0.124 ppm indicates that
the area is expected to attain the standard. This type of test is often
referred to as an exceedance test. The EPA's guidance recommends that
States use either of two modeled attainment or exceedance tests for the
one-hour ozone NAAQS: a deterministic test or a statistical test.
The deterministic test requires the State to compare predicted one-
hour daily maximum ozone concentrations for each modeled day
8 to the attainment level of 0.124 ppm. If none of the
predictions exceed 0.124 ppm, the test is passed.
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\8\ The initial, ``ramp-up'' days for each episode are excluded
from this determination.
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The statistical test takes into account the fact that the form of
the one-hour ozone standard allows exceedances. If, over a three-year
period, the area has an average of one or fewer exceedances per year,
the area is not violating the standard. Thus, if the State models a
very extreme day, the statistical test provides that a prediction above
0.124 ppm up to a certain upper limit may be consistent with attainment
of the standard. (The form of the one-hour standard allows for up to
three readings above the standard over a three-year period before an
area is considered to be in violation.)
The acceptable upper limit above 0.124 ppm is determined by
examining the size of exceedances at monitoring sites which meet the
one-hour NAAQS. For example, a monitoring site for which the four
highest one-hour average concentrations over a three-year period are
0.136 ppm, 0.130 ppm, 0.128 ppm and 0.122 ppm is attaining the
standard. To identify an acceptable upper limit, the statistical
likelihood of observing ozone air quality exceedances of the standard
of various concentrations is equated to the severity of the modeled
day. The upper limit generally represents the maximum ozone
concentration observed at a location on a single day and it would be
the only reading above the standard that would be expected to occur no
more than an average of once a year over a three-year period.
Therefore, if the maximum ozone concentration predicted by the model is
below the acceptable upper limit, in this case 0.136 ppm, then EPA
might conclude that the modeled attainment test is passed. Generally,
exceedances well above 0.124 ppm are very unusual at monitoring sites
meeting the NAAQS. Thus, these upper limits are rarely substantially
higher than the attainment level of 0.124 ppm.
2. Additional Analyses Where Modeling Fails To Show Attainment
When the modeling does not conclusively demonstrate attainment,
additional analyses may be presented to help determine whether the area
will attain the standard. As with other predictive tools, there are
inherent uncertainties associated with modeling and its results. For
example, there are uncertainties in some of the modeling inputs, such
as the meteorological and emissions data bases for individual days and
in the methodology used to assess the severity of an exceedance at
individual sites. The EPA's guidance recognizes these limitations, and
provides a means for considering other evidence to help assess whether
attainment of the NAAQS is likely. The process by which this is done is
called a weight of evidence (WOE) determination.
Under a WOE determination, the State can rely on and EPA will
consider factors such as: other modeled attainment tests, e.g., a
rollback analysis; other modeled outputs, e.g., changes in the
predicted frequency and pervasiveness of exceedances and predicted
changes in the design value;
[[Page 70323]]
actual observed air quality trends; estimated emissions trends;
analyses of air quality monitored data; the responsiveness of the model
predictions to further controls; and, whether there are additional
control measures that are or will be approved into the SIP but were not
included in the modeling analysis. This list is not an exclusive list
of factors that may be considered and these factors could vary from
case to case. The EPA's guidance contains no limit on how close a
modeled attainment test must be to passing to conclude that other
evidence besides an attainment test is sufficiently compelling to
suggest attainment. However, the further a modeled attainment test is
from being passed, the more compelling the WOE needs to be.
The EPA's 1996 modeling guidance also recognizes a need to perform
a mid-course review as a means for addressing uncertainty in the
modeling results. Because of the uncertainty in long term projections,
EPA believes a viable attainment demonstration that relies on WOE needs
to contain provisions for periodic review of monitoring, emissions, and
modeling data to assess the extent to which refinements to emission
control measures are needed. The mid-course review is discussed in
Section C.6.
C. What Is the Frame Work for Proposing Action on the Attainment
Demonstration SIPs?
In addition to the modeling analysis and WOE support demonstrating
attainment, the EPA has identified the following key elements which
generally must be present in order for EPA to approve or conditionally
approve the one-hour attainment demonstration SIPs. These elements are
listed below and then described in detail.
--CAA measures and measures relied on in the modeled attainment
demonstration SIP. This includes adopted and submitted rules for all
previously required CAA mandated measures for the specific area
classification. This also includes measures that may not be required
for the area classification but that the State relied on in the SIP
submission for attainment and ROP plans on which EPA is proposing to
take action on today.
--NOX reductions affecting boundary conditions.
--Motor vehicle emissions budget. A motor vehicle emissions budget
which can be determined by EPA to be adequate for conformity purposes.
--Tier 2/Sulfur program benefits where needed to demonstrate
attainment. Inclusion of reductions expected from EPA's Tier 2 tailpipe
and low sulfur-in-fuel standards in the attainment demonstration and
the motor vehicle emissions budget, if needed for attainment.
--In certain areas, additional measures to further reduce emissions to
support the attainment test. Additional measures may be measures
adopted regionally such as in the Ozone Transport Region (OTR), or
locally (intrastate) in individual States.
--Mid-Course Review (MCR). An enforceable commitment to conduct a mid-
course review and evaluation based on air quality and emission trends.
The mid-course review would show whether the adopted control measures
are sufficient to reach attainment by the area's attainment date, or
that additional control measures are necessary.
1. CAA Measures and Measures Relied on in the Modeled Attainment
Demonstration SIP
The States should have adopted the control measures already
required under the CAA for the area classification. Since these 10
serious and severe areas need to achieve substantial reductions from
their 1990 emissions levels in order to attain, EPA anticipates that
these areas need all of the measures required under the CAA to attain
the one-hour ozone NAAQS.
In addition, a state may have included control measures in its
attainment strategy that are in addition to measures required in the
CAA. (For serious areas, these should have already been identified and
adopted, whereas severe areas have until December 2000 to submit
measures necessary to achieve ROP through the attainment year and to
attain.) For purposes of fully approving the State's SIP, the State
will need to adopt and submit all VOC and NOX controls
within the local modeling domain that were relied on for purposes of
the modeled attainment demonstration.
The information in Table 1 is a summary of the CAA requirements
that need to be met for each serious area for the one-hour ozone NAAQS.
These requirements are specified in section 182 of the CAA. Information
on more measures that States may have adopted or relied on in their
current SIP submissions is not shown in the table. EPA will need to
take final action approving all measures relied on for attainment,
including the required ROP control measures and target calculations,
before EPA can issue a final full approval of the attainment
demonstration as meeting CAA section 182(c)(2).
Table 1.--CAA Requirements for Serious Areas
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--NSR for VOC and NOX \1\, including an offset ratio of 1.2:1 and a
major VOC and NOX source cutoff of 50 tons per year (tpy).
--Reasonable Available Control Technology (RACT) for VOC and NOX \1\.
--Enhanced Inspection and Maintenance (I/M) program.
--15% volatile organic compound (VOC) plans.
--Emissions inventory.
--Emission statements.
--Periodic inventories.
--Attainment demonstration.
--9 percent ROP plan through 1999.
--Clean fuels program or substitute.
--Enhanced monitoring Photochemical Assessment Monitoring Stations
(PAMS).
--Stage II vapor recovery
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\1\ Unless the area has in effect a NOX waiver under section 182(f).
Western Massachusetts is not such an area.
2. NOX Reductions Consistent With the Modeling Demonstration
The EPA completed final rulemaking on the NOX SIP call
on October 27, 1998, which required States to address transport of
NOX and ozone to other States. To address transport, the
NOX SIP call established emissions budgets for
NOX that 23 jurisdictions were required to show they would
meet through enforceable SIP measures adopted and submitted by
September 30, 1999. The NOX SIP call is intended to reduce
emissions in upwind States that significantly contribute to
nonattainment problems. The EPA did not identify specific sources that
the States must regulate nor did EPA limit the States' choices
regarding where to achieve the emission reductions. Subsequently, a
three-judge panel of the Court of Appeals for the District of Columbia
Circuit issued an order staying the portion of the NOX SIP
call rule requiring States to submit rules by September 30, 1999.
The NOX SIP call rule establishes budgets for the States
in which 9 of the nonattainment areas for which EPA is proposing action
today are located. The 9 areas are: Greater Connecticut, Springfield
MA, New York-North New Jersey-Long Island (NY-NJ-CT), Baltimore MD,
Philadelphia-Wilmington-Trenton (PA-NJ-DE-MD), Metropolitan Washington,
D.C. (DC-MD-VA), Atlanta GA, Milwaukee-Racine WI, and Chicago-Gary-Lake
County (IL-IN).
Emission reductions that will be achieved through EPA's
NOX SIP call will reduce the levels of ozone and ozone
precursors entering nonattainment areas at their boundaries.
[[Page 70324]]
For purposes of developing attainment demonstrations, States define
local modeling domains that include both the nonattainment area and
nearby surrounding areas. The ozone levels at the boundary of the local
modeling domain are reflected in modeled attainment demonstrations and
are referred to as boundary conditions. With the exception of Houston,
the one-hour attainment demonstrations on which EPA is proposing action
have relied, in part, on the NOX SIP Call reductions for
purposes of determining the boundary conditions of the modeling domain.
Emission reductions assumed in the attainment demonstrations are
modeled to occur both within the State and in upwind States; thus,
intrastate reductions as well as reductions in other States impact the
boundary conditions. Although the court has indefinitely stayed the SIP
submission deadline, the NOX SIP Call rule remains in
effect. Therefore, EPA believes it is appropriate to allow States to
continue to assume the reductions from the NOX SIP call in
areas outside the local one-hour modeling domains. If States assume
control levels and emission reductions other than those of the
NOX SIP call within their State but outside of the modeling
domain, States must also adopt control measures to achieve those
reductions in order to have an approvable plan.
Accordingly, States in which the nonattainment areas are located
will not be required to adopt measures outside the modeling domain to
achieve the NOX SIP call budgets prior to the time that all
States are required to comply with the NOX SIP call. If the
reductions from the NOX SIP call do not occur as planned,
States will need to revise their SIPs to add additional local measures
or obtain interstate reductions, or both, in order to provide
sufficient reductions needed for attainment.
As provided in section 1 above, any controls assumed by the State
inside the local modeling domain 9 for purposes of the
modeled attainment demonstration must be adopted and submitted as part
of the State's one-hour attainment demonstration SIP. It is only for
reductions occurring outside the local modeling domain that States may
assume implementation of NOX SIP call measures and the
resulting boundary conditions.
---------------------------------------------------------------------------
\9\ For the purposes of this document, ``local modeling domain''
is typically an urban scale domain with horizontal dimensions less
than about 300 km on a side, horizontal grid resolution less than or
equal to 5 x 5 km or finer. The domain is large enough to ensure
that emissions occurring at 8 am in the domain's center are still
within the domain at 8 pm the same day. If recirculation of the
nonattainment area's previous day's emissions is believed to
contribute to an observed problem, the domain is large enough to
characterize this.
---------------------------------------------------------------------------
3. Motor Vehicle Emissions Budget
The EPA believes that attainment demonstration SIPs must
necessarily estimate the motor vehicle emissions that will be produced
in the attainment year and demonstrate that this emissions level, when
considered with emissions from all other sources, is consistent with
attainment. The estimate of motor vehicle emissions is used to
determine the conformity of transportation plans and programs to the
SIP, as described by CAA section 176(c)(2)(A). For transportation
conformity purposes, the estimate of motor vehicle emissions is known
as the motor vehicle emissions budget. The EPA believes that
appropriately identified motor vehicle emissions budgets are a
necessary part of an attainment demonstration SIP. A SIP cannot
effectively demonstrate attainment unless it identifies the level of
motor vehicle emissions that can be produced while still demonstrating
attainment.
The EPA has determined that except for the Springfield (Western
Massachusetts) attainment demonstration SIP, the motor vehicle emission
budgets for all areas in today's proposals are inadequate or missing
from the attainment demonstration. Therefore, EPA is proposing to
disapprove the attainment demonstration SIPs for those areas if the
States do not submit motor vehicle emissions budgets that EPA can find
adequate by May 31, 2000. A 2003 motor vehicle emission budget was
submitted for the Western Massachusetts nonattainment area on October
1, 1998 and determined to be adequate by EPA on February 19, 1999.
4. Tier 2/Sulfur Program Benefits
On May 13, 1999, EPA published a Notice of Proposed Rulemaking
(NPRM) proposing a major, comprehensive program designed to
significantly reduce emissions from passenger cars and light trucks
(including sport-utility vehicles, minivans, and pickup trucks) and to
reduce sulfur in gasoline. Under the proposed program, automakers would
produce vehicles designed to have very low emissions when operated on
low-sulfur gasoline, and oil refiners would provide that cleaner
gasoline nationwide. The EPA subsequently issued two supplemental
notices. 64 FR 35112 (June 30, 1999); 64 FR 57827 (October 27, 1999).
These notices provide one-hour ozone modeling and monitoring
information that support EPA's belief that the Tier 2/Sulfur program is
necessary to help areas attain the one-hour NAAQS. Under the proposed
rule, NOX and VOC emission reductions (as well as other
reductions not directly relevant for attainment of the one-hour ozone
standard) would occur beginning in the 2004 ozone season although
incentives for early compliance by vehicle manufacturers and refiners
will likely result in some reductions prior to 2004. Nationwide, the
Tier 2/Sulfur program is projected to result in reductions of
approximately 800,000 tons of NOX per year by 2007 and
1,200,000 tons by 2010.
In the October 27, 1999 supplemental notice, EPA reported in Table
1 that EPA's regional ozone modeling indicated that 17 metropolitan
areas for which the one-hour standard applies need the Tier 2/Sulfur
program reductions to help attain the one-hour ozone standard. The
Springfield (Western Massachusetts) area was included on that list. On
August 13, 1999, the MA DEP submitted a letter requesting an attainment
date extension until December 2003, which is before the Tier 2/Sulfur
reductions occur. Massachusetts believes that violations of the ozone
standard will be eliminated by that time frame. Therefore, the Tier 2/
Sulfur reductions are not being relied upon for attainment of the one-
hour standard by Massachusetts.
5. Additional Measures to Further Reduce Emissions
The EPA is proposing to find that the attainment demonstrations for
New York-North New Jersey-Long Island; Baltimore; Philadelphia-
Wilmington-Trenton; Houston-Galveston-Brazoria and Atlanta, even
considering the Tier 2/Sulfur program reductions and the WOE, will not
achieve attainment without the application of additional emission
control measures to achieve additional emission reductions. Thus, for
each of these areas, EPA has identified specific tons per day emissions
of NOX and/or VOC that must be reduced through additional
control measures in order to demonstrate attainment and to enable EPA
to approve the demonstration. The need for additional emission
reductions is generally based on a lack of sufficient compelling
evidence that the demonstration shows attainment at the current level
of adopted or planned emission controls.
As discussed below the Springfield (Western Massachusetts) area
does contain compelling evidence that attainment will be attained by
its proposed attainment date of December 31, 2003, and additional
reductions are
[[Page 70325]]
not needed to demonstrate attainment. The details for the Western
Massachusetts area are discussed below.
6. Mid-Course Review
A mid-course review (MCR) is a reassessment of modeling analyses
and more recent monitored data to determine if a prescribed control
strategy is resulting in emission reductions and air quality
improvements needed to attain the ambient air quality standard for
ozone as expeditiously as practicable but no later than the statutory
dates. For serious areas such as Springfield (Western Massachusetts)
requesting an attainment date extension to a year prior to 2005, a
review that occurs at a midpoint prior to the attainment date would be
impractical in terms of timing. Therefore, for these areas, EPA is
looking for a commitment to perform an early attainment assessment to
be submitted by the end of the attainment year (i.e., 2003). In
addition, EPA believes the state should commit to work with EPA in a
public consultative process to develop a methodology for performing the
early attainment assessment and developing the criteria by which
adequate progress would be judged.
Massachusetts submitted a commitment with its July 28, 1998
attainment demonstration committing to assess the progress and
implementation of the state and federal measures necessary for
attainment. Massachusetts committed to perform this assessment by
November, 2001. EPA encourages Massachusetts to perform this assessment
at the end of 2003, the date requested by Massachusetts for attainment.
D. What Does EPA Expect to Happen With Respect to the Attainment
Demonstration for the Springfield (Western Massachusetts) One-hour
Ozone Nonattainment Area?
Table 2 shows a summary of information on what EPA expects from
States to allow EPA to approve the one-hour ozone attainment
demonstration SIPs. As explained in the Table, Massachusetts has
already completed the actions due by December 31, 1999.
Table 2.--Summary Schedule of Future State Actions--Serious Nonattainment Areas
----------------------------------------------------------------------------------------------------------------
Req'd no later than Action
----------------------------------------------------------------------------------------------------------------
12/31/99......................................................... State submits the following to EPA:
--Motor vehicle emissions budget
(Massachusetts submitted its emissions
budget on October 1, 1998).
--Commitment to do the following:
--Perform an early attainment assessment at
the end of the attainment year
(Massachusetts submitted a commitment with
its July 28, 1998 attainment demonstration
committing to assess the progress and
implementation of the state and federal
measures necessary for attainment).
12/31/03......................................................... State submits an early attainment assessment
at the end of the attainment year.
----------------------------------------------------------------------------------------------------------------
E. What Are the Relevant Policy and Guidance Documents?
This proposal has cited several policy and guidance memoranda. The
EPA has also developed several technical documents related to the
rulemaking action in this proposal. Some of the documents have been
referenced above. The documents and their location on EPA's web site
are listed below; these documents will also be placed in the docket for
this proposal action.
Recent Documents
1. ``Guidance for Improving Weight of Evidence Through
Identification of Additional Emission Reductions, Not Modeled.'' U.S.
Environmental Protection Agency, Office of Air Quality Planning and
Standards, Emissions, Monitoring, and Analysis Division, Air Quality
Modeling Group, Research Triangle Park, NC 27711. November 1999. Web
site: http://www.epa.gov/ttn/scram (file name: ``ADDWOE1H'').
2. ``Serious and Severe Ozone Nonattainment Areas: Information on
Emissions, Control Measures Adopted or Planned and Other Available
Control Measures.'' Draft Report. November 3, 1999. Ozone Policy and
Strategies Group. U.S. EPA, RTP, NC.
3. Memorandum, ``Guidance on Motor Vehicle Emissions Budgets in
One-Hour Attainment Demonstrations,'' from Merrylin Zaw-Mon, Office of
Mobile Sources, to the Air Division Directors, Regions I-VI. November
3, 1999. Web site: http://www.epa.gov/oms/transp/trafconf.html.
4. Memorandum from Lydia Wegman and Merrylin Zaw-Mon to the Air
Division Directors, Regions I-VI, ``1-Hour Ozone Attainment
Demonstrations and Tier 2/Sulfur Rulemaking.'' November 8, 1999. Web
site: http://www.epa.gov/oms/transp/trafconf.html.
5. Draft Memorandum, ``Analyses To Support Mid-course Review Of
SIP's To Meet The 1-hr NAAQS For Ozone.'' From John Seitz, Director,
Office of Air Quality Planning and Standards. Web site: http://
www.epa.gov/ttn/scram (file name: ``DR6MCR'').
6. Memorandum, ``Guidance on the Reasonably Available Control
Measures (RACM) Requirement and Attainment Demonstration Submissions
for Ozone Nonattainment Areas.'' John S. Seitz, Director, Office of Air
Quality Planning and Standards. November 30, 1999. Web site: http://
www.epa.gov/ttn/oarpg/t1pgm.html.
Previous Documents
1. U.S. EPA, (1991), Guideline for Regulatory Application of the
Urban Airshed Model, EPA-450/4-91-013, (July 1991). Web site: http://
www.epa.gov/ttn/scram/ (file name: ``UAMREG'').
2. U.S. EPA, (1996), Guidance on Use of Modeled Results to
Demonstrate Attainment of the Ozone NAAQS, EPA-454/B-95-007, (June
1996). Web site: http://www.epa.gov/ttn/scram/ (file name: ``O3TEST'').
3. Memorandum, ``Ozone Attainment Demonstrations,'' from Mary D.
Nichols, issued March 2, 1995. Web site: http://www.epa.gov/ttn/oarpg/
t1pgm.html.
4. Memorandum, ``Extension of Attainment Dates for Downwind
Transport Areas,'' issued July 16, 1998. Web site: http://www.epa.gov/
ttn/oarpg/t1pgm.html.
5. December 29, 1997 Memorandum from Richard Wilson, Acting
Assistant Administrator for Air and Radiation ``Guidance for
Implementing the 1-Hour Ozone and Pre-Existing PM10 NAAQS.''
Web site: http://www.epa.gov/ttn/oarpg/t1pgm.html.
II. How Does the Massachusetts Submittal Satisfy the Frame Work?
This section provides a review of Massachusetts' submittal and an
[[Page 70326]]
analysis of how this submittal satisfies the frame work discussed in
Section I. of this notice.
A. What Did The State Submit?
The attainment demonstration SIP submitted by the Massachusetts
Department of Environmental Protection for the Western Massachusetts
area includes a modeling analysis using the CALGRID model. This was
submitted on July 27, 1998. The SIP was subject to public notice and
comment and a hearing was held in June 1998. Information on how the
photochemical grid modeling meets EPA guidance is summarized below.
Massachusetts also requested an attainment date extension for this area
on August 13, 1999. The state requested a new attainment date of
December 2003, which EPA interprets as December 31, 2003. This
submittal was subject to public notice and comment. This attainment
date extension is discussed below.
B. What Did the Attainment Demonstration SIP Contain?
The one-hour attainment demonstration submitted by Massachusetts is
for both the Boston (Eastern Massachusetts) serious area as well as the
Springfield (Western Massachusetts) serious area. The Eastern
Massachusetts serious area, however, has air quality better than the
one-hour standard and in June 1999, EPA issued a final rule determining
that the 1-hour ozone standard no longer applied (64 FR 30911) and that
Boston no longer needed a one-hour attainment demonstration. EPA has
since proposed to reinstate the standard (64 FR 57424). However, even
if the one-hour standard is reinstated, Eastern Massachusetts would
continue to qualify, based on recent air quality data, as a clean data
area under the EPA policy related to ozone nonattainment areas meeting
the one-hour ozone NAAQS (May 10, 1995) and the attainment
demonstration requirement would be deferred pending redesignation.
The key element of the attainment demonstration is the
photochemical grid point modeling required by the CAA. The
Massachusetts SIP used the CALGRID model which was approved for use by
EPA since it was found to be at least as effective as the guideline
model which is UAM-IV. The modeling domain for CALGRID extends from
southwest Connecticut, northward 340 km to northern Vermont, and
eastward to east of Nantucket, Massachusetts. For the Western
Massachusetts nonattainment area, the domain meets EPA guidance since
it contains adequate areas both upwind and downwind of the
nonattainment area. The domain also includes the monitors with the
highest measured peak ozone concentrations in Massachusetts and coastal
Maine and New Hampshire. Since the original modeling was done for a
much larger domain that includes not only all of Massachusetts but also
includes all of Rhode Island, most of Connecticut, southern New
Hampshire, southern Vermont, and most of southern Maine, the CALGRID
model has several ``source'' areas and several receptor areas. The only
receptor area of import to this notice and the Springfield (Western
Massachusetts) SIP submittal is the Western Massachusetts area, which
includes the following Counties: Berkshire, Franklin, Hampshire and
Hampden. For the purposes of this notice, only model results in this
four county area will be used, unless otherwise noted. As shown below,
EPA believes the modeling portion of the attainment demonstration meets
EPA guidance.
The model was run for 10 days during four distinct episodes (August
14-17, 1987, June 21-22, 1988, July 7-8, 1988 and July 10-11, 1988).
These episodes represent a variety of ozone conducive weather
conditions, and also include the three worst ranked ozone episodes
(1987 to 1998) for the domain. The episodes selected reflect days with
high measured ozone in a variety of areas within the entire domain.
This is because, as stated above, the domain covers several
nonattainment areas, and in order to model the meteorology that causes
high ozone, several different episodes were needed. The model results
for the first day of each episode are not used for attainment
demonstration purposes, because they are considered ``ramp-up days.''
Ramp-up days help reduce impacts of initial conditions; after ramp-up
days, model results are more reflective of actual emissions being
emitted into the atmosphere.
The two key episodes for purposes of assessing whether attainment
with the one-hour ozone standard can be achieved are the two July 1988
episodes. This is because these two episodes can use the boundary
conditions generated using the modeling done by EPA for OTAG. At the
time of the CALGRID modeling, the OTAG modeling was the best regional
scale ozone modeling that was available for boundary conditions. OTAG
boundary conditions give the best representation of expected future
year emissions in upwind areas and certain runs can be used to simulate
the effects of the NOX SIP call promulgated by EPA on
October 27, 1998 (63 FR 57356). The other two episodes can not use this
newer and better regional modeling for boundary conditions, because
OTAG did not model these episodes, and therefore no OTAG boundary
conditions are available. For those episodes, the older Regional
Oxidant Model (ROM) boundary conditions are used to reflect future
benefits from CAA measures. However, there are no ROM boundary
conditions that adequately reflect EPA's NOX SIP call.
Since the best boundary conditions are from OTAG, only two episodes
remain relevant for further discussion (July 7-8, 1988 and July 10-11,
1988). Only one of these episodes is relevant to Western Massachusetts
and that is the July 7-8, 1988 episode. The July 10-11, 1988 episode
had less impact on Western Massachusetts and is more an Eastern
Massachusetts and coastal New England episode. As stated above, the
model domain was set up in the early 1990's with many nonattainment
areas in mind (the Rhode Island serious area, the Eastern Massachusetts
serious area, the Portsmouth-Dover-Rochester serious area in New
Hampshire and three moderate areas in Maine). The Western Massachusetts
area was only one of these competing for episode days.
The CALGRID model was run using the CALMET meteorological
processor. This processor took actual meteorological data collected by
the National Weather Service and the State Air Pollution Agencies and
using extrapolation and other analysis techniques provided winds,
temperatures and other meteorological parameters at approximately 400
specific grid points for each hour of the episode at up to 14 levels
from the surface to top of the model about 5000 feet. CALMET is
described in detail in the Massachusetts attainment demonstration, and
was approved by EPA for use in the CALGRID modeling system.
The CALGRID model was run with emissions data prepared by EPA
Region I and/or a contractor working with EPA Region I. The data were
taken from the EPA Aerometric Informational Retrieval System (AIRS)
data base in late 1993 and reflect the emission data supplied from the
six New England States. The emission data for the small portion of New
York state that forms the western edge of the domain was supplied by
New York. EPA Region I quality assured all the New England AIRS data,
the New York supplied data and all necessary modifications to the data.
The data was further processed through EPS's Emissions Preprocessor
System (EPS Version 2.0). To more accurately model ozone in New
England, day specific
[[Page 70327]]
emissions were simulated for on-road mobile sources (cars, trucks,
busses, etc.), and for large power plants in New England.
Future emissions were projected to 1999 accounting for both
emission increases due to industrial growth, population growth and
growth in the number of miles traveled by cars, as well as emission
reductions due to cleaner gasoline, cleaner cars and controls on
industrial pollution. Growth factors were derived using the EPA-
approved Bureau of Economic Analysis (BEA) factors and all the
emissions were processed using the EPS 2.0 system.
Model runs were also performed for the year 2007. Year 2007
emissions estimates were prepared by the states reflecting EPA's
proposed NOX SIP call (62 FR 60318, November 7, 1997). This
was accomplished using a two step process. The first step was to
project emissions using growth factors to account for increases or
decreases in economic activity by industrial sector. In general, the
states projected their emissions using the same growth factors that
were used in the OTAG modeling effort. The second step involved
applying control factors to source categories that would be regulated
by the year 2007. States used a combination of information for control
levels: those used for the OTAG modeling effort, and state-specific
information relating to the effectiveness of control programs planned
or in place.
C. What Are the Conclusions From the Modeling?
The EPA guidance for approval of the modeling aspect of a one-hour
ozone attainment demonstration is to use the one-hour ozone grid
modeling to apply one of two modeled attainment tests (deterministic or
statistical) with optional weight of evidence analyses to supplement
the modeled attainment test results when the modeled attainment test is
failed. The modeling performed for the Western Massachusetts area does
not show attainment of the one-hour ozone standard (124 ppb) at every
grid cell for every hour of every episode day modeled. Maximum
predicted concentrations in western Massachusetts for the relevant
episode (July 8, 1988) are 135 ppb. Using the statistical test
described above, this is slightly above the acceptable upper limit for
that day of 130 ppb.
However, when Massachusetts' weight of evidence analysis is
considered, attainment is adequately demonstrated. One of the elements
in a weight of evidence analysis is use of the model predicted change
in ozone to estimate a future air quality design value. This uses the
air quality modeling in a relative sense. The highest design value in
Western Massachusetts, based on 1995 to 1997 monitoring data, was 132
ppb. The model shows that, with the planned emission reductions in the
two precursor emissions (VOC and NOX), ground-level ozone
concentrations will be lowered to approximately 119 ppb.
More specifically, to strengthen the weight of evidence analyses,
the Massachusetts attainment demonstration uses the model predictions
in a relative sense to estimate a future design value. This type of
analysis is sometimes referred to as a local rollback analysis. It uses
the local CALGRID modeling to predict future values (i.e., rollback the
current design value) of the current ozone design value. The DEP
compared two CALGRID runs to estimate the improvement in ozone air
quality levels that would occur after 1999 due to continued
implementation of CAA controls within the New England modeling domain (
the modeling domain includes most of CT, NH and VT, all of MA and RI
and southern ME) and due to controls pursuant to EPA's NOX
SIP call both within the domain and upwind of the domain. The first run
used 1999 emission files coupled with 2007 boundary conditions from
OTAG modeling just reflecting Clean Air Act controls. 10 The
1999 runs for the two July episodes were then compared with the
modeling runs done for 2007 using: (1) 2007 boundary conditions from
OTAG modeling reflecting Clean Air Act controls and NOX
reductions equivalent to the regional NOX SIP call adopted
by EPA, and (2) 2007 emissions within the modeling domain reflecting
Clean Air Act controls and NOX reductions equivalent to the
regional NOX SIP call. This comparison showed that recent
air quality design values can reasonably be expected to be reduced
below 124 ppb based solely on continued additional reductions within
the domain (e.g., areas in CT, western MA) subsequent to 1999 and
reductions from EPA's NOX SIP call. Not taken credit for in
the analysis is benefits from CAA controls upwind of the New England
modeling domain that occur after 1999 (e.g., phase 2 reformulated
gasoline, benefits from new automobile standards, etc.) making the
analysis conservative since reductions from such programs in areas
immediately upwind of the modeling domain (i.e., areas in New York and
New Jersey) will help Western Massachusetts attain the one-hour ozone
standard. The modeling also indicates that ozone reductions from
emission reductions in the New England domain would be greater if
boundary conditions were cleaner. So emission reduction from future
programs like the Tier 2/Sulfur program would further aid in reaching
and maintaining attainment of the one-hour ozone standard after 2003.
---------------------------------------------------------------------------
\10\ Note that the 1999 emission files did not include I/M
emission reductions for an enhanced I/M program in Massachusetts
since this program will not be fully implemented until some time
after 1999.
---------------------------------------------------------------------------
In summary, based on a weight-of-evidence analysis, the modeling
submitted for the Springfield (Western Massachusetts) area meets the
EPA guidance and is acceptable.
D. What Do the Ambient Ozone Data Show?
The weight of evidence analysis conducted by Massachusetts is
consistent with the most recent ozone data. There are five ozone air
quality monitors in the Western Massachusetts nonattainment area. They
are in the towns of Chicopee, Agawam, Ware, Adams and Amherst. The
monitor in Adams is in a mountaintop location and has only recorded two
exceedances of the one-hour ozone standard since 1989 and is clearly in
attainment with the ozone standard and therefore is not an issue with
respect to attainment/nonattainment. The other four monitors were all
recording violations of the one-hour ozone standard when the area was
classified as serious in 1991 (based on ozone data from circa 1987 to
1989). Since the original classification all these sites have shown a
substantial decrease in ozone due to emission reductions, both within
Massachusetts and also upwind from Massachusetts. For example, the site
at Agawam has shown a design value (the form of the one-hour ozone
standard) drop from 148 ppb in 1989 to 110 ppb in 1998 or a drop of
26%. This site is currently in attainment for the one-hour standard. At
Chicopee, the design value has dropped from 159 ppb to 116 ppb in 1998,
a drop of 27%. This site is also attainment. At Amherst the design
value has dropped from 135 ppb to 106 ppb in 1998 for a drop of 21%.
This site is in attainment. At the Ware site the design value has
dropped from 167 ppb to 128 ppb in 1999, for a drop of 23%. This is the
only site in Western Massachusetts that is still recording violations
of the ozone standard. A linear fit of those two design values (167 ppb
in 1989 and 128 ppb in 1998) shows a drop of nearly 4 ppb per year of
ozone. Since the Ware site is currently only 4 ppb over the one-hour
ozone standard, attainment of the standard may be expected with in the
[[Page 70328]]
next two years (i.e., by 2001). It must be noted that the year to year
decline in ozone levels is rarely linear and year to year variations do
occur, but, since these four ozone sites all show a substantial
downward trend in one-hour ozone concentrations, and precursor
emissions are projected to keep falling, both within the nonattainment
area and upwind from it, there is no reason to believe that this
downward trend will not continue over the near term. The emission
reductions will be a result of the following: continued benefits from
tighter standards on vehicles due to fleet turnover (California (CA)
LEV in Massachusetts and NLEV or CA LEV in upwind areas); the
reductions from large point sources due to the OTC NOX
Memorandum of Understanding (MOU) and EPA's NOX SIP call;
Phase II reformulated gasoline; ultimately Tier 2 automobile standards
and low sulfur gasoline; and other federal control measures (i.e.,
controls on non-road engines). In addition, Massachusetts started an
enhanced I/M program in October 1999 which will also yield emission
reductions.
E. Does the Area Need Additional Measures?
Since the Western Massachusetts area passes the weight-of evidence
test it does not need additional measures, including Tier 2 automobile
standards.
F. What Is EPA Policy With Regards to an Attainment Date Extension?
On July 16, 1998, a guidance memorandum entitled ``Extension of
Attainment Dates for Downwind Transport Areas'' was signed by Richard
D. Wilson, then Acting Assistant Administrator for Air and Radiation.
That memorandum included EPA's interpretation of the Clean Air Act
regarding the possibility of extending attainment dates for ozone
nonattainment areas that have been classified as moderate or serious
for the 1-hour standard and which are downwind of areas that have
interfered with their ability to demonstrate attainment by dates
prescribed in the Act. That memorandum stated that EPA will consider
extending the attainment date for an area that:
(1) Has been identified as a downwind area affected by transport
from either an upwind area in the same State with a later attainment
date or an upwind area in another State that significantly contributes
to downwind nonattainment;
(2) Has submitted an approvable attainment demonstration with any
necessary, adopted local measures and with an attainment date that
shows that it will attain the 1-hour standard no later than the date
that the reductions are expected from upwind areas under the final
NOX SIP call and/or the statutory attainment date for upwind
nonattainment areas, i.e., assuming the boundary conditions reflecting
those upwind reductions;
(3) Has adopted all applicable local measures required under the
area's current classification and any additional measures necessary to
demonstrate attainment, assuming the reductions occur as required in
the upwind areas;
(4) Has provided that it will implement all adopted measures as
expeditiously as practicable, but no later than the date by which the
upwind reductions needed for attainment will be achieved.
G. Does the Western Massachusetts Area Qualify for an Attainment Date
Extension?
The following analysis shows that the area does meet the above four
part test. In its July 27, 1998 attainment demonstration, the MA DEP
requested that, since the Western Massachusetts area cannot attain the
one-hour ozone standard by its attainment date of 1999, due to the
effects of transported ozone, it be allowed an attainment date
extension beyond 1999. On August 13, 1999 the MA DEP submitted a letter
requesting an attainment date extension to December 2003, which EPA
interprets as December 31, 2003. This date matches the MA DEP
conformity budget submitted to EPA on October 1, 1998 and is in line
with most of the emission reductions expected as a result of the
NOX SIP call.
In order to qualify for an attainment date extension several tests
need to be passed. In order to assess the role of transport in Western
Massachusetts, two model runs submitted by Massachusetts are examined.
The first is a zero out run for Connecticut. In this run, all the
anthropogenic emissions from the nearest upwind state are eliminated.
This run shows only limited improvement in the Western Massachusetts
area from such a large emission reduction. Another run that shows the
impact of transport in Western Massachusetts is a run where very clean
boundary conditions are assumed. This run uses boundary conditions from
the OTAG run IN60, which assumed the reductions similar to
NOX SIP call emissions, plus an additional 60% reduction in
NOX from the ozone nonattainment areas classified as serious
or above. This run shows that Western Massachusetts would achieve
attainment by 2007, based on a strict exceedance test (i.e., all grid
cells below 124 ppb). Thus, it is transported air pollution that is
causing the area to be nonattainment and that transport is from upwind
areas outside the modeling domain (e.g., New York City). Therefore,
lowering transported ozone is extremely important in bringing Western
Massachusetts into attainment of the ozone standard. In summary, the
Western Massachusetts area is affected by transport. So the first test
for an attainment date extension is passed.
The second test is that an area has submitted an approvable
attainment demonstration with any necessary, adopted local measures and
with an attainment date that shows that it will attain the one-hour
standard no later than the date that the reductions are expected from
upwind areas under the final NOX SIP call and/or the
statutory attainment date for upwind nonattainment areas, i.e.,
assuming the boundary conditions reflecting those upwind reductions.
Since the area has submitted an attainment demonstration and this
notice is proposing approval of that plan without additional measures,
this test is passed. Also, since the attainment date requested is
December 2003, which is in line with the NOX SIP call and
the Phase III NOX MOU requirements, that date is reasonable.
The third test is that Massachusetts had to do all the CAA requires
for a serious nonattainment area. The Western Massachusetts area is
classified as serious and is required to submit certain measures. Table
3 contains a summary of the CAA required ozone SIP elements and the
additional measures included in the attainment demonstration. This
Table indicates whether a control measure was part of the modeling
demonstration and provides a summary of the approval or promulgation
status.
[[Page 70329]]
Table 3.--Control Measures in the One-Hour Ozone Attainment Plans for the Western Massachusetts Serious Ozone
Nonattainment Area
----------------------------------------------------------------------------------------------------------------
Included in local
Name of control measure Type of measure modeling Approval status
----------------------------------------------------------------------------------------------------------------
On-board Refueling Vapor Recovery.. Federal rule.......... Yes................... Promulgated at 40 CFR 86.
Federal Motor Vehicle Control Federal rule.......... Yes................... Promulgated at 40 CFR 86.
program.
Federal Non-road Gasoline Engines.. Federal rule.......... Yes................... Promulgated at 40 CFR 90.
Federal Non-road Heavy Duty diesel Federal rule.......... Yes................... Promulgated at 40 CFR 89.
engines.
AIM Surface Coatings............... State initiative...... Yes................... SIP approved (60 FR 65242;
12/19/95).
Consumer & commercial products..... State initiative...... Yes................... SIP approved (60 FR 65242;
12/19/95).
Enhanced Inspection & Maintenance.. CAA SIP Requirement... Yes................... SIP approval pending
(proposed for approval at
64 FR 51937; 9/27/99 and
64 FR 66829; 11/30/99)
\1\.
NOX RACT........................... CAA SIP Requirement... Yes................... SIP approved (64 FR 48095;
9/2/99).
VOC RACT pursuant to sections CAA SIP Requirement... Yes................... SIP approved (64 FR 48297;
182(a)(2)(A) and 182(b)(2)(B) of 9/3/99 and 58 FR 34908; 6/
Clean Air Act. 30/93).
VOC RACT pursuant to sections CAA SIP Requirement... Yes................... SIP approved (64 FR 48297;
182(b)(2)(A) and (C) of Clean Air 9/3/99).
Act.
Stage II Vapor Recovery............ CAA SIP Requirement... Yes................... SIP approved (58 FR 48315;
9/15/93) \2\.
Automotive Refinishing............. State initiative...... Yes................... SIP approved (61 FR 5696; 2/
14/96).
Reformulated Gasoline.............. State opt-in.......... Yes................... SIP approval pending
(proposed for approval as
part of the 15% plan at 64
FR 51943; 9/27/99 and 64
FR 66829;11/30/99).
CA Low Emission Vehicle (CA LEV)... State initiative...... Yes................... SIP approved (60 FR 6027; 2/
1/95).
Clean Fuel Fleets.................. CAA SIP Requirement... Yes................... SIP approved (60 FR 6027; 2/
1/95) \3\.
New Source Review.................. CAA SIP Requirement... No.................... SIP approval pending \4\.
Base Year Emissions Inventory...... CAA SIP Requirement... N/A \5\............... SIP approved (62 FR 37510;
7/14/97).
15% VOC Reduction Plan............. CAA SIP Requirement... Yes\6\................ SIP approval pending
(proposed for approval at
64 FR 51943; 9/27/99 and
64 FR 66829; 11/30/99).
9% rate of progress plan........... CAA SIP Requirement... Yes \6\............... SIP approval pending
(proposed for approval at
64 FR 51943; 9/27/99 and
64 FR 66829;11/30/99)).
Emissions Statements............... CAA SIP Requirement... N/A 5................. SIP approved (61 FR 11556;
3/21/96).
Enhanced Monitoring (PAMS)......... CAA Requirement....... N/A 5................. SIP approved (62 FR 37510;
7/14/97).
OTC NOX MOU Phase II............... State initiative...... Yes................... SIP approved (64 FR 6/2/99;
64 FR 29567).
NOX SIP Call....................... EPA requirement....... Yes................... SIP approval pending \7\.
----------------------------------------------------------------------------------------------------------------
\1\ Massachusetts Enhanced Inspection & Maintenance was proposed for approval based on a showing that their
program meets EPA's low enhanced performance standard and secures the emission reduction necessary to meet 15%
and 9% rate-of-progress requirements. Massachusetts, however, is claiming reductions greater than these
amounts in its attainment demonstration. Massachusetts needs to demonstrate that the emission reduction credit
it is claiming from its I/M program in its attainment demonstration is warranted for the combination of test
type and equipment that Massachusetts is implementing. On November 3, 1999, MA DEP sent a letter to EPA
indicating that it expects submit its I/M program evaluation plan by March 31, 2000. EPA expects that the
program evaluation done pursuant to the plan will enable Massachusetts to demonstrate the level of emission
reduction credit warranted for its I/M program.
\2\ In its Attainment Demonstration SIP submittal, Massachusetts committed to submit a revised Stage II rule by
January 1999. Massachusetts has not yet met this commitment but must do so in order for EPA to grant final
approval of its attainment demonstration for Western Massachusetts. On November 24, 1999, MA DEP sent a letter
to EPA indicating that it expects to adopt the necessary revisions to its stage II rule by April 1, 2000.
\3\ Massachusetts used CAL LEV reductions to meet the Clean Fuel Fleet requirement.
\4\ The state is not relying on emission reductions from this NSR SIP and therefore it will not have to be
finally approved in order to approve the attainment demonstration.
\5\ Does not produce emission reductions.
\6\ The measures used to demonstrate rate of progress were modeled.
\7\ On November 19, 1999, MA DEP submitted a SIP revision in response to the EPA's regulation entitled,
``Finding of Significant Contribution and Rulemaking for Certain States in the Ozone Transport Assessment
Group Region for Purposes of Reducing Regional Transport of Ozone,'' otherwise known as the ``NOX SIP Call.''
The SIP submittal included a NOX budget and allowance trading regulation, 310 CMR 7.28. Although not a CAA
required measure, 310 CMR 7.28 requires significant NOX reductions from 2003 onward which will strengthen the
SIP. EPA will take final action on 310 CMR 7.28 prior to finalizing action on the one-hour ozone attainment
plan. This also fulfills Massachusetts commitment under the OTC MOU Phase III program.
For the measures that have been submitted to EPA and not yet fully
approved by EPA, EPA intends to publish final rules before or at the
same time as we publish final approval of the attainment demonstration.
Those include the 15% plan and 9% plan through 1999, the enhanced
inspection and maintenance program, and the NOX SIP call
SIP. Additionally, there are additional SIP elements that have not been
submitted by Massachusetts that EPA needs in order to agree with the
reductions claimed by Massachusetts for certain control programs.
Because of these outstanding elements, EPA is also proposing, in the
alternative, to disapprove this demonstration. These outstanding SIP
elements are: (1) Revisions to the Massachusetts stage II vapor
recovery rule that were
[[Page 70330]]
committed to in the July 27, 1998 attainment demonstration and (2) the
demonstration described in EPA's supplementary proposed approval of the
Massachusetts 15% rate-of-progress plan published in the Federal
Register on November 30, 1999 (64 FR 66829), requiring Massachusetts to
demonstrate that the emission reduction credit it is claiming for its
I/M program in that attainment demonstration is warranted for the
combination of test type and equipment that Massachusetts is
implementing. Once these outstanding SIP elements are approved into the
Massachusetts SIP, the attainment demonstration can be approved and the
attainment date extension to December 31, 2003 can be granted.
Finally, the state has provided that it will implement all adopted
measures as expeditiously as practicable, but no later than the date by
which the upwind reductions needed for attainment will be achieved. All
of the above measures will be implemented by December 2003.
In summary, EPA is proposing to approve the new attainment date of
December 31, 2003 for the area. In order to grant full approval, the
outstanding SIP issues mentioned above will need to be resolved.
H. What Are the Consequences of State Failure?
This section explains the CAA consequences of State failure to meet
the time frames and terms described generally in this notice. The CAA
provides for the imposition of sanctions and the promulgation of a
federal implementation plan if States fail to submit a required plan,
submit a plan that is determined to be incomplete or if EPA disapproves
a plan. (We using the phrase ``failure to submit'' to cover both the
situation where a State makes no submission and the situation where the
State makes a submission that we find is incomplete in accordance with
section 110(k)(1)(B) and 40 CFR part 51, Appendix V.) For purposes of
sanctions, there are no sanctions clocks in place based on a failure to
submit. Thus, the description of the timing of sanctions, below, is
linked to a potential disapproval of the State's submission.
1. What Are the CAA's Provisions for Sanctions?
If EPA disapproves a required SIP, such as the attainment
demonstration SIPs, section 179(a) provides for the imposition of two
sanctions. The first sanction would apply 18 months after EPA
disapproves the SIP if the State fails to make the required submittal
which EPA proposes to fully or conditionally approve within that time.
Under EPA's sanctions regulations, 40 CFR 52.31, the first sanction
would be 2:1 offsets for sources subject to the new source review
requirements under section 173 of the CAA. If the State has still
failed to submit a SIP for which EPA proposes full or conditional
approval 6 months after the first sanction is imposed, the second
sanction will apply. The second sanction is a limitation on the receipt
of Federal highway funds. EPA also has authority under section 110(m)
to a broader area, but is not proposing to take such action today.
2. What Are the CAA's FIP Provisions if a State Fails To Submit a Plan?
In addition to sanctions, if EPA finds that a State failed to
submit the required SIP revision or disapproves the required SIP
revision EPA must promulgate a FIP no later than 2 years from the date
of the finding if the deficiency has not been corrected. The attainment
demonstration SIPs on which EPA is taking action today were originally
due in November 1994. However, through a series of policy memoranda,
EPA recognized that States had not submitted attainment demonstrations
and were constrained to do so until ozone transport had been further
analyzed. As provided in the Background, above, EPA provided for States
to submit the attainment demonstration SIPs in two phases. In June
1996, EPA made findings that ten States and the District of Columbia
had failed to submit the phase I SIPs for nine nonattainment areas. 61
FR 36292 (July 10, 1996). In addition on May 19, 1997, EPA made a
similar finding for Pennsylvania for the Philadelphia area. 62 FR
27201.
In July 1998, several environmental groups filed a notice of
citizen suit, alleging that EPA had outstanding sanctions and FIP
obligations for the serious and severe nonattainment areas on which EPA
is proposing action today. These groups filed a lawsuit in the Federal
District Court for the District of Columbia on November 8, 1999.
III. Proposed Action
EPA is proposing to approve the ground-level one-hour ozone
attainment demonstration State implementation plan (SIP or
demonstration) for the Springfield (Western Massachusetts)
nonattainment area submitted by Massachusetts on July 27, 1998. We are
also proposing to approve an attainment date extension for this area to
December 31, 2003 submitted by Massachusetts on August 13, 1999. We are
also proposing, in the alternative, to approve in part and disapprove
in part this demonstration if the State does not submit the following
elements which were discussed in detail above: revisions to the
Massachusetts stage II vapor recovery rule and a demonstration
adequately proving that the emission reduction credit Massachusetts is
claiming from its I/M program in the Western Massachusetts attainment
demonstration is warranted for the combination of test type and
equipment that Massachusetts is implementing. Also, EPA intends to
publish final rulemaking on the 15% plan and 9% plan through 1999, the
enhanced inspection and maintenance program, and the NOX SIP
call SIP for Western Massachusetts either before or at the same time as
publication of final approval of the attainment demonstration.
EPA is soliciting public comments on the issues discussed in this
proposal or on other relevant matters. These issues will be considered
before EPA takes final action. Interested parties may participate in
the Federal rulemaking procedure by submitting written comments to the
EPA Regional office listed in the ADDRESSES section of this action.
A more detailed description of the state submittal and EPA's
evaluation are included in a Technical Support Document (TSD) prepared
in support of this rulemaking action. A copy of the TSD is available
upon request from the EPA Regional Office listed in the ADDRESSES
section of this document.
Nothing in this action should be construed as permitting or
allowing or establishing a precedent for any future request for
revision to any State implementation plan. Each request for revision to
the State implementation plan shall be considered separately in light
of specific technical, economic, and environmental factors and in
relation to relevant statutory and regulatory requirements.
IV. Administrative Requirements
A. Executive Order 12866
The Office of Management and Budget (OMB) has exempted this
regulatory action from review under Executive Order 12866, entitled
``Regulatory Planning and Review.''
B. Executive Order 13045
Executive Order 13045, entitled ``Protection of Children from
Environmental Health Risks and Safety Risks'' (62 FR 19885, April 23,
1997), applies to any rule that the EPA determines (1) is
``economically significant,'' as defined under Executive Order 12866,
and (2) the environmental health or safety risk addressed by the
[[Page 70331]]
rule has a disproportionate effect on children. If the regulatory
action meets both criteria, the Agency must evaluate the environmental
health or safety effects of the planned rule on children and explain
why the planned regulation is preferable to other potentially effective
and reasonably feasible alternatives considered by the Agency.
This final rule is not subject to Executive Order 13045 because it
does not involve decisions intended to mitigate environmental health
and safety risks.
C. Executive Order 13084
Under Executive Order 13084, EPA may not issue a regulation that is
not required by statute, that significantly affects or uniquely affects
the communities of Indian tribal governments, and that imposes
substantial direct compliance costs on those communities, unless the
Federal government provides the funds necessary to pay the direct
compliance costs incurred by the tribal governments. If the mandate is
unfunded, EPA must provide to the Office of Management and Budget, in a
separately identified section of the preamble to the rule, a
description of the extent of EPA's prior consultation with
representatives of affected tribal governments, a summary of the nature
of their concerns, and a statement supporting the need to issue the
regulation. In addition, Executive Order 13084 requires EPA to develop
an effective process permitting elected and other representatives of
Indian tribal governments ``to provide meaningful and timely input in
the development of regulatory policies on matters that significantly or
uniquely affect their communities.'' Today's rule does not
significantly or uniquely affect the communities of Indian tribal
governments. This action does not involve or impose any requirements
that affect Indian Tribes. Accordingly, the requirements of section
3(b) of Executive Order 13084 do not apply to this rule.
D. Executive Order 13132
Executive Order 13132 Federalism (64 FR 43255, August 10, 1999),
revokes and replaces Executive Orders 12612 (Federalism) and 12875
(Enhancing the Intergovernmental Partnership). Executive Order 13132
requires EPA to develop an accountable process to ensure ``meaningful
and timely input by State and local officials in the development of
regulatory policies that have federalism implications.'' ``Policies
that have federalism implications'' is defined in the Executive Order
to include regulations that have ``substantial direct effects on the
States, on the relationship between the national government and the
States, or on the distribution of power and responsibilities among the
various levels of government.'' Under Executive Order 13132, EPA may
not issue a regulation that has federalism implications, that imposes
substantial direct compliance costs, and that is not required by
statute, unless the Federal government provides the funds necessary to
pay the direct compliance costs incurred by State and local
governments, or EPA consults with State and local officials early in
the process of developing the proposed regulation. EPA also may not
issue a regulation that has federalism implications and that preempts
State law unless the Agency consults with State and local officials
early in the process of developing the proposed regulation.
This rule will not have substantial direct effects on the States,
on the relationship between the national government and the States, or
on the distribution of power and responsibilities among the various
levels of government, as specified in Executive Order 13132 (64 FR
43255, August 10, 1999), because it merely approves a State rule
implementing a federal standard, and does not alter the relationship or
the distribution of power and responsibilities established in the Clean
Air Act. Thus, the requirements of section 6 of the Executive Order do
not apply to this rule.
E. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA) generally requires an agency
to conduct a regulatory flexibility analysis of any rule subject to
notice and comment rulemaking requirements unless the agency certifies
that the rule will not have a significant economic impact on a
substantial number of small entities. Small entities include small
businesses, small not-for-profit enterprises, and small governmental
jurisdictions. This proposed rule will not have a significant impact on
a substantial number of small entities because SIP approvals under
section 110 and subchapter I, part D of the Clean Air Act do not create
any new requirements but simply approve requirements that the State is
already imposing. Therefore, because the Federal SIP approval does not
create any new requirements, I certify that this action will not have a
significant economic impact on a substantial number of small entities.
Moreover, due to the nature of the Federal-State relationship under the
Clean Air Act, preparation of a flexibility analysis would constitute
Federal inquiry into the economic reasonableness of state action. The
Clean Air Act forbids EPA to base its actions concerning SIPs on such
grounds. Union Electric Co. v. U.S. EPA, 427 U.S. 246, 255-66 (1976);
42 U.S.C. 7410(a)(2).
If the approval is converted to a disapproval under section 110(k),
based on the State's failure to meet the commitment, it will not affect
any existing State requirements applicable to small entities. Federal
disapproval of the State submittal does not affect State-
enforceability. Moreover, EPA's disapproval of the submittal does not
impose any new requirements. Therefore, I certify that such a
disapproval action will not have a significant economic impact on a
substantial number of small entities because it would not remove
existing requirements nor would it substitute a new Federal
requirement.
The EPA's alternative proposed disapproval of the State request
under section 110 and subchapter I, part D of the Act would not affect
any existing requirements applicable to small entities. Any pre-
existing Federal requirements would remain in place after this
disapproval. Federal disapproval of the State submittal would not
affect State-enforceability. Moreover EPA's disapproval of the
submittal does not impose any new Federal requirements. Therefore, I
certify that the proposed disapproval would not have a significant
impact on a substantial number of small entities.
F. Unfunded Mandates
Under section 202 of the Unfunded Mandates Reform Act of 1995
(``Unfunded Mandates Act''), signed into law on March 22, 1995, EPA
must prepare a budgetary impact statement to accompany any proposed or
final rule that includes a Federal mandate that may result in estimated
annual costs to State, local, or tribal governments in the aggregate;
or to private sector, of $100 million or more. Under section 205, EPA
must select the most cost-effective and least burdensome alternative
that achieves the objectives of the rule and is consistent with
statutory requirements. Section 203 requires EPA to establish a plan
for informing and advising any small governments that may be
significantly or uniquely impacted by the rule.
EPA has determined that the proposed approval action does not
include a Federal mandate that may result in estimated annual costs of
$100 million or more to either State, local, or tribal governments in
the aggregate, or
[[Page 70332]]
to the private sector. This Federal action approves pre-existing
requirements under State or local law, and imposes no new requirements.
Accordingly, no additional costs to State, local, or tribal
governments, or to the private sector, result from this action.
Sections 202 and 205 do not apply to the proposed disapproval
because the proposed disapproval of the SIP submittal would not, in and
of itself, constitute a Federal mandate because it would not impose an
enforceable duty on any entity. In addition, the Act does not permit
EPA to consider types of analyses described in section 202 in
determining whether a SIP submittal meets the CAA. Finally, section 203
does not apply to the proposed disapproval because it would affect only
the Commonwealth of Massachusetts, which is not a small government.
G. National Technology Transfer and Advancement Act
Section 12 of the National Technology Transfer and Advancement Act
(NTTAA) of 1995 requires Federal agencies to evaluate existing
technical standards when developing new regulations. To comply with
NTTAA, the EPA must consider and use ``voluntary consensus standards''
(VCS) if available and applicable when developing programs and policies
unless doing so would be inconsistent with applicable law or otherwise
impractical.
EPA believes that VCS are inapplicable to this action. Today's
action does not require the public to perform activities conducive to
the use of VCS.
List of Subjects in 40 CFR Part 52
Environmental protection, Air pollution control, Hydrocarbons,
Intergovernmental relations, Nitrogen dioxide, Ozone.
Authority: 42 U.S.C. 7401 et seq.
Dated: November 30, 1999.
Mindy S. Lubber,
Deputy Regional Administrator, Region I.
[FR Doc. 99-31709 Filed 12-15-99; 8:45 am]
BILLING CODE 6560-50-P
