Approval and Promulgation of Implementation Plans; Klamath Falls, Oregon Nonattainment Area; Fine Particulate Matter Emissions Inventory and SIP Strengthening Measures, 78372-78376 [2014-30498]
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Federal Register / Vol. 79, No. 249 / Tuesday, December 30, 2014 / Proposed Rules
issue a Notice of Enforcement with an
updated enforcement schedule.
(c) Regulations.
(1) In accordance with the general
regulations in § 165.23 of this part, entry
into, transiting, or anchoring in this
safety zone is prohibited unless
authorized by the Captain of the Port
Lake Michigan or her designated onscene representative.
(2) This safety zone is closed to all
vessel traffic except as permitted by the
Captain of the Port Lake Michigan or her
designated on-scene representative.
(3) The ‘‘on-scene representative’’ of
the Captain of the Port Lake Michigan
is any Coast Guard commissioned,
warrant, or petty officer who has been
designated by the Captain of the Port
Lake Michigan to act on her behalf. The
Captain of the Port Lake Michigan or her
designated on-scene representative may
be contacted via VHF Channel 16.
(4) Vessel operators desiring to enter
or operate within the safety zone shall
contact the Captain of the Port Lake
Michigan or her designated on-scene
representative to obtain permission to
do so. Vessel operators given permission
to enter or operate in the safety zone
must comply with all directions given to
them by the Captain of the Port Lake
Michigan or her on-scene
representative.
Dated: December 3, 2014.
A.B. Cocanour,
Captain, U. S. Coast Guard, Captain of the
Port Lake Michigan.
[FR Doc. 2014–30491 Filed 12–29–14; 8:45 am]
BILLING CODE 9110–04–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R10–OAR–2013–0005; FRL–9920–97–
Region 10]
Approval and Promulgation of
Implementation Plans; Klamath Falls,
Oregon Nonattainment Area; Fine
Particulate Matter Emissions Inventory
and SIP Strengthening Measures
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
The Oregon Department of
Environmental Quality (ODEQ)
submitted a revision to the State
Implementation Plan (SIP), dated
December 14, 2012, to address Clean Air
Act (CAA or the Act) requirements for
the Klamath Falls, Oregon
nonattainment area for the 2006 24-hour
fine particulate matter (PM2.5) national
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SUMMARY:
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ambient air quality standard (NAAQS).
The EPA proposes to approve the
emissions inventory contained in the
ODEQ’s submittal as meeting the
requirement to submit a comprehensive,
accurate, and current inventory of direct
PM2.5 and PM2.5 precursor emissions in
Klamath Falls, Oregon. The EPA also
proposes to approve PM2.5 control
measures contained in the December
2012 submittal because incorporation of
these measures will strengthen the
Oregon SIP and reduce sources of PM2.5
emissions in the Klamath Falls, Oregon
nonattainment area (Klamath Falls
NAA) that contribute to violations of the
2006 PM2.5 NAAQS.
DATES: Comments must be received on
or before January 29, 2015.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–R10–
OAR–2013–0005, by any of the
following methods:
• www.regulations.gov: Follow the
on-line instructions for submitting
comments.
• Email: R10-Public_Comments@
epa.gov.
• Mail: Justin A. Spenillo, EPA
Region 10, Office of Air, Waste and
Toxics (AWT–150), 1200 Sixth Avenue,
Suite 900, Seattle, WA 98101.
• Hand Delivery/Courier: EPA Region
10, 1200 Sixth Avenue, Suite 900,
Seattle, WA 98101. Attention: Justin A.
Spenillo, Office of Air, Waste and
Toxics, AWT–150. Such deliveries are
only accepted during normal hours of
operation, and special arrangements
should be made for deliveries of boxed
information
Instructions: Direct your comments to
Docket ID No. EPA–R10–OAR–2013–
0005. The EPA’s policy is that all
comments received will be included in
the public docket without change and
may be made available online at
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
the disclosure of which is restricted by
statute. Do not submit information that
you consider to be CBI or otherwise
protected through www.regulations.gov
or email. The www.regulations.gov Web
site is an ‘‘anonymous access’’ system,
which means the EPA will not know
your identity or contact information
unless you provide it in the body of
your comment. If you send an email
comment directly to the EPA without
going through www.regulations.gov your
email address will be automatically
captured and included as part of the
comment that is placed in the public
docket and made available on the
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Internet. If you submit an electronic
comment, the EPA recommends that
you include your name and other
contact information in the body of your
comment and with any disk or CD–ROM
you submit. If the EPA cannot read your
comment due to technical difficulties
and cannot contact you for clarification,
the EPA may not be able to consider
your comment. Electronic files should
avoid the use of special characters, any
form of encryption, and be free of any
defects or viruses.
Docket: All documents in the docket
are listed in the www.regulations.gov
index. Although listed in the index,
some information is not publicly
available, e.g., CBI or other information,
the disclosure of which is restricted by
statute. Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy. Publicly
available docket materials are available
either electronically in
www.regulations.gov or in hard copy
during normal business hours at the
Office of Air, Waste and Toxics, EPA
Region 10, 1200 Sixth Avenue, Seattle
WA, 98101.
FOR FURTHER INFORMATION CONTACT:
Justin A. Spenillo at (206) 553–6125,
spenillo.justin@epa.gov, or the above
EPA, Region 10 address.
SUPPLEMENTARY INFORMATION:
Throughout this document whenever
‘‘we,’’ ‘‘us,’’ or ‘‘our’’ is used, we mean
the EPA.
Table of Contents
I. Background
A. PM2.5 National Ambient Air Quality
Standards
B. Designation of PM2.5 Nonattainment
Areas
C. Submittal Requirements for PM2.5
Nonattainment Areas
II. Analysis of the State’s Submittal
A. Emissions Inventory
B. Description of the Klamath County PM2.5
Control Measures
III. Proposed Action
IV. Statutory and Executive Order Reviews
I. Background
A. PM2.5 National Ambient Air Quality
Standards
Under section 109 of the CAA, the
EPA establishes NAAQS for certain
pervasive air pollutants (referred to as
‘‘criteria pollutants’’) and conducts
periodic reviews of the NAAQS to
determine whether they should be
revised or whether new NAAQS should
be established. After a new NAAQS is
established or an existing NAAQS is
revised, all areas across the country are
evaluated to determine whether they
meet the new or revised standard, and
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area designations are promulgated based
on that evaluation.
On July 18, 1997, the EPA revised the
NAAQS for particulate matter to add
new standards for fine particles, using
PM2.5 (particles less than or equal to 2.5
micrometers in aerodynamic diameter)
as the indicator for the pollutant. The
EPA established primary and
secondary 1 annual and 24-hour
standards for PM2.5 (62 FR 38652). The
annual standard was set at 15.0
micrograms per cubic meter (mg/m3),
based on a 3-year average of the annual
mean PM2.5 concentrations, and the 24hour standard was set at 65 mg/m3,
based on the 3-year average of the 98th
percentile of 24-hour PM2.5
concentrations. On October 17, 2006,
the EPA revised the level of the 24-hour
PM2.5 NAAQS to 35 mg/m3, based on a
3-year average of the 98th percentile of
24-hour concentrations (71 FR 61144).
On December 14, 2012, the EPA revised
the primary annual PM2.5 NAAQS to
provide increased protection of public
health and welfare from fine particle
pollution (78 FR 3086, January 15,
2013). In that action, the EPA revised
the primary annual PM2.5 standard,
strengthening it from 15.0 micrograms
per cubic meter (mg/m3) to 12.0 mg/m3,
which is attained when the 3-year
average of the annual arithmetic means
does not exceed 12.0 mg/m3.
B. Designation of PM2.5 Nonattainment
Areas
Effective December 14, 2009, the EPA
established the initial air quality
designations for most areas in the
United States for the 2006 24-hour PM2.5
NAAQS (74 FR 58688, November 13,
2009). The Klamath Falls area was
designated nonattainment for the 2006
24-hour PM2.5 NAAQS. The boundaries
for this area are described in 40 CFR
81.338.
C. Submittal Requirements for PM2.5
Nonattainment Areas
In March 2012, the EPA issued
guidance to states for implementation of
the 2006 PM2.5 NAAQS (March 2012
Implementation Guidance).2 The
guidance recommended that states make
submissions for the 2006 PM2.5 NAAQS
consistent with the substantive
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1 For
a given air pollutant, ‘‘primary’’ national
ambient air quality standards are those determined
by the EPA as requisite to protect the public health,
and ‘‘secondary’’ standards are those determined by
the EPA as requisite to protect the public welfare
from any known or anticipated adverse effects
associated with the presence of such air pollutant
in the ambient air. See CAA section 109(b).
2 Memorandum from Stephen D. Page,
Implementation Guidance for the 2006 24-Hour
Fine Particulate (PM2.5) National Ambient Air
Quality Standards (Mar. 2, 2012).
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requirements developed for
implementation of the 1997 PM2.5
NAAQS at 40 CFR part 51, subpart Z
(Provisions for Implementation of PM2.5
National Ambient Air Quality
Standards, 40 CFR 51.1000, et seq.). In
December 2012, based on the March
2012 Implementation Guidance, the
ODEQ submitted a SIP revision
intended to address the nonattainment
planning requirements for the Klamath
Falls NAA.
On January 4, 2013, the Court of
Appeals for the District of Columbia
remanded to the EPA the Clean Air Fine
Particle Implementation Rule (72 FR
20586, Apr. 25, 2007) (hereafter referred
to as the ‘‘PM2.5 implementation rule’’)
which formed the basis of the 40 CFR
part 51, subpart Z nonattainment
planning requirements. Natural
Resources Defense Council v. EPA, 706
F.3d 428 (D.C. Cir. 2013). The Court
concluded that the EPA had improperly
based the PM2.5 implementation rule
solely upon the requirements of part D,
subpart 1 of the CAA, and had failed to
address the requirements of part D,
subpart 4. As a result of the Court’s
remand of the PM2.5 implementation
rule, the EPA withdrew its March 2012
Implementation Guidance because it
was based largely on the remanded rule
promulgated to implement the 1997
PM2.5 NAAQS.3 The EPA is currently
engaged in rulemaking to address the
Court’s remand of the PM2.5
implementation rule. In the interim,
however, the EPA continues to take
action on SIP submissions from states
intended to address nonattainment
planning requirements for the 2006
PM2.5 NAAQS, consistent with the CAA.
This action is limited to proposing
approval of the emissions inventory of
direct PM2.5 and PM2.5 precursors
submitted by the ODEQ for the Klamath
Falls NAA as required under section
172(c)(3) of the CAA, and the approval
of specific control measures that are
expected to strengthen the SIP. These
control measures independently meet
requirements for control measures in
attainment plans and the emissions
reductions they achieve will contribute
to attainment of the 2006 PM2.5 NAAQS
in the Klamath Falls NAA.
II. Analysis of the State’s Submittal
A. Emissions Inventory
The EPA promulgated emissions
inventory requirements for the 1997
PM2.5 NAAQS as part of the PM2.5
implementation rule at 40 CFR 51.1008.
3 Memorandum from Stephen D. Page,
Withdrawal of Implementation Guidance for the
2006 24-Hour Fine Particle (PM2.5) National
Ambient Air Quality Standards (Jun. 6, 2013).
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The decision in NRDC v. EPA remanded
the PM2.5 implementation rule because
it did not incorporate the specific
particulate matter requirements of
subpart 4, part D, title I. The emission
inventory requirements set forth in the
PM2.5 implementation rule were based
on the CAA section 172(c)(3)
requirements in subpart 1. Subpart 4
contains no specific provision governing
emissions inventories for PM10 or PM2.5
nonattainment areas that supersedes the
general emissions inventory
requirement for all nonattainment areas
in section 172(c)(3). See ‘‘State
Implementation Plans; General
Preamble for the Implementation of
Title I of the Clean Air Act Amendments
of 1990,’’ (57 FR 13498, 13539, April 16,
1992) (hereinafter ‘‘General Preamble’’).
Accordingly, the EPA is evaluating the
ODEQ’s emissions inventory for the
Klamath Falls NAA pursuant to the
CAA requirements in section 172(c)(3).
Section 172(c)(3) of the CAA requires
a state with an area designated as
nonattainment to submit to the EPA for
approval a comprehensive, accurate,
and current inventory of actual
emissions of the pollutant at issue,
including emissions of any precursor of
that pollutant, for the nonattainment
area. These inventories provide a
detailed accounting of all emissions and
emissions sources by pollutant and
precursor pollutant within the
nonattainment area. In addition,
inventories are used to model air quality
to demonstrate attainment of the 2006
PM2.5 NAAQS as expeditiously as
practicable. The EPA reviewed, in
accordance with the August 2005 EPA
guidance, ‘‘Emissions Inventory
Guidance for Implementation of Ozone
and Particulate Matter NAAQS and
Regional Haze Regulations,’’ the
procedures and methodologies used by
the ODEQ to develop the emission
inventory for the 2008 base year
emissions inventory for the Klamath
Falls NAA. In accordance with section
172(c)(3) and consistent with EPA
guidance, Oregon’s attainment plan as
described below includes a
comprehensive, accurate, and current
inventory of emissions of all direct
PM2.5 and PM2.5 precursors in the
Klamath Falls NAA.
To develop an emissions inventory
that matches the conditions under
which the design value concentration
are measured, the ODEQ emissions
inventory addresses annual emissions,
typical season day emissions, and worst
case day emissions. Annual emissions,
measured in tons per year (‘‘tpy’’), are
the total amount of emissions over the
course of a calendar year. The typical
season day and worst-case day
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emissions are measured in pounds (lbs)
per day and are calculated for the PM
season, which is the four-month period
between November and February when
ambient PM concentrations from
anthropogenic sources are generally the
highest. Typical season day emissions
are the average emissions over the fourmonth PM season, and worst case day
emissions are the amount emitted on
winter days with a diurnal temperature
range representative of PM2.5
exceedances. Most source categories are
modeled using the typical season day
emissions. Worst-case day emissions are
better suited for select sources, such as
residential wood combustion and motor
vehicles, with emissions highly
dependent on temperature. At colder
temperatures there is a behavioral
increase in home heating using
woodstoves, and vehicle emissions
associated with start-up emissions are
higher on colder days.
The year 2008 was selected by ODEQ
as the base year for the emissions
inventory because it was the most recent
year that Oregon completed the NEI data
submittal prior to the designation of the
Klamath Falls NAA in 2009. The
selection of 2008 as the baseline year for
the emissions inventory is consistent
with the emissions inventory
requirement in section 172(c)(3) because
it provides an inventory of emissions for
one of the years relied upon for the
nonattainment designation. The ODEQ’s
2008 base year emissions inventory
includes emissions of direct PM2.5 and
PM2.5 precursors that cover the general
source categories of stationary point
sources, stationary nonpoint sources
(area sources), non-road mobile sources,
and on-road mobile sources. The main
sources of emissions in the Klamath
Falls NAA are residential wood
combustion, mobile and non-road
sources, and point sources. The
pollutants that comprise the 2008 base
year inventory include direct PM2.5 and
the precursors to the formation of PM2.5
which are nitrogen oxide (NOX), volatile
organic compounds (VOCs), ammonia
(NH3), and sulfur dioxide (SO2).
The point source inventory provides
facility-specific data for point source
emissions from Klamath Falls’
permitted stationary sources. Permitted
point sources include industrial
sources, non-industrial sources, gas
stations, crematories, and portable
sources. The emissions inventory
includes actual point source emissions
for both the annual and the seasonal
inventory. For purposes of the worstcase day emission inventory, the
emissions for permitted point sources
are reported at 80% of the permitted
operating capacity because such specific
daily actual emissions are not available
for permitted point sources in the same
manner as annual and typical season
emissions. The EPA agrees that 80% of
permitted emissions is a conservative
estimate for worst-case day actual
emissions and, given that permitted
point sources were not found to be
significantly contributing to the
monitored violations. This will be
further discussed in a future notice
when the EPA acts on the ODEQ’s
control strategy for the Klamath Falls
NAA.
The complete inventory, located in
the docket for this rulemaking, also
includes a description of minor nonpermitted point sources. Area sources
for the Klamath Falls NAA are divided
into six groups: Waste disposal,
treatment and recovery; small stationary
fossil fuel combustion; residential wood
combustion; fugitive dust; evaporative/
off-gassing emissions sources; and
miscellaneous area sources. The on-road
mobile source emissions inventory
includes all sources of mobile exhaust,
brake, and tire emissions generated by
passenger vehicles, trucks,
miscellaneous vehicles, and reentrained road dust. Non-road mobile
sources inventoried include aircraft,
gasoline and diesel-powered vehicles
and equipment, recreational marine
vessels, and trains.
The ODEQ compiled the emissions
inventory relying on information from a
variety of sources. Permitted point
source emissions data were taken from
the ODEQ Tracking Reporting and
Administration of Air Contaminant
Sources (TRAACS) database which is
submitted to the EPA National
Emissions Inventory System. Many area
source emissions were taken from the
2008 EPA National Emissions Inventory
(NEI) v.1.5. The ODEQ Area Mobile
Emissions Estimates (AMEE) database
was also a source of emissions data for
mobile emissions. Additional emissions
information was taken from a 2007/2008
residential wood combustion survey
and from use of the EPA Motor Vehicle
Emission Simulator (MOVES). All
remaining emissions were modeled or
inventoried specifically for this
attainment plan. The full emissions
inventory submitted by the ODEQ and
a detailed description of the
methodology used to compile the
inventory is presented in Attachment
3.3l of the SIP submittal included in the
docket for this action.
Table 1 summarizes the annual
emissions for Klamath Falls in 2008 and
Table 2 summarizes the worst-case day
emissions for Klamath Falls in 2008.
Typical season day emissions
information can be found in Attachment
3.3l of the SIP submittal included in the
docket for this action.
TABLE 1—2008 KLAMATH FALLS, ANNUAL EMISSIONS
[tpy]
Source sector
PM2.5
SOX
NOX
NH3
VOC
143.4
403.0
92.2
16.1
47.8
49.1
6.4
6.6
329.3
114.3
1,431.6
360.9
70.4
161.9
11.4
........................
997.2
972.9
694.2
246.0
Total ..............................................................................
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Point .....................................................................................
Area ......................................................................................
Onroad .................................................................................
Nonroad ...............................................................................
654.7
109.9
2,236.1
243.7
2,910.4
TABLE 2—2008 KLAMATH FALLS, WORST-CASE DAY
[lbs/day]
Source sector
PM2.5
Point .....................................................................................
Area ......................................................................................
Onroad .................................................................................
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SOX
1,517
2,851
917
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NOX
357
546
36
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NH3
3,247
1,391
7,990
30DEP1
1,453
772
62
VOC
10,301
6,483
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TABLE 2—2008 KLAMATH FALLS, WORST-CASE DAY—Continued
[lbs/day]
Source sector
SOX
PM2.5
NOX
NH3
VOC
Nonroad ...............................................................................
135
108
2,855
........................
876
Total ..............................................................................
5,420
1,046
15,483
2,287
22,754
The EPA reviewed the results,
procedures and methodologies for the
2008 base year emissions inventory in
accordance with the EPA’s current
guidance, ‘‘Emissions Inventory
Guidance for Implementation of Ozone
and Particulate Matter NAAQS and
Regional Haze Regulations’’ (August
2005). The ODEQ used standard
procedures to develop the emissions
inventory and appropriately used
seasonal and worst-case day emissions
inventories to represent episodic
meteorological conditions when PM2.5
levels are of the greatest concern. For
this reason, the EPA is proposing
approval of Klamath Falls’ 2008 base
year emissions inventory as meeting the
requirements of section 172(c)(3) of the
CAA.
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B. Description of the Klamath County
PM2.5 Control Measures
On December 12, 2012, the ODEQ
submitted to the EPA for approval
revisions to a number of rules related to
the Klamath Falls NAA. These revisions
consist of updates to identify the
Klamath Falls NAA and to adopt local
and state measures to ensure permanent
and enforceable control strategies
intended to bring the area back into
attainment through control of PM2.5 and
its precursors. Specifically, the ODEQ
revised rules in Oregon Administrative
Rules (OAR) Chapter 340, Divisions 200,
204, 225, 240, 262, and 264. These
revisions, and the EPA’s proposed
actions on them, are described below.
Division 204: Designation of Air Quality
Areas
The ODEQ revised OAR Chapter 340,
Division 204 to include a description of
the Klamath Falls PM2.5 NAA boundary.
The EPA proposes to approve and
incorporate by reference (IBR) this
revision into the SIP because the area
description is essential for delineating
the nonattainment area, and we believe
the area description is consistent with
the EPA description in the designation
for the area.
Division 225: Air Quality Analysis
Requirements
The ODEQ revised OAR 340–225–
0090, in conjunction with promulgating
OAR 340–240–0550, as encouragement
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for direct PM10 and PM2.5 emissions
reductions from residential wood-fired
devices as a means to offset, in an equal
or greater amount, emissions increases
from new major sources or major
modifications to major sources located
in the Klamath Falls NAA, provided
such sources do not cause or contribute
to a violation of the NAAQS. The
revisions to OAR 340–225–0090 exempt
a source which proposes to use
qualifying woodstove offsets from the
need to conduct an air dispersion
modeling analysis to demonstrate a net
air quality benefit as would otherwise
be required. Woodstove emissions are
the primary source of PM2.5 emissions
contributing to NAAQS violations in the
NAA and reductions in woodstove
emissions would presumptively result
in a net air quality benefit when used to
offset new emissions from a stationary
source located within the NAA. A
source proposing to use other sources of
emission offsets, or woodstove offsets
that don’t meet the requirements of OAR
340–240–0550, would still need to
conduct a dispersion modeling analysis
to demonstrate a net air quality benefit.
The revisions are designed to maintain
and promote continued air quality
improvement while allowing for
economic growth that does not
negatively affect the airshed.
In a letter dated September 15, 2014,
Oregon withdrew the submitted SIP
revision for OAR 340–225–
0090(2)(a)(C). Accordingly, the EPA is
not acting on the revisions to OAR 340–
225–0090(2)(a)(C) which establish interpollutant offset ratios. Oregon may
submit a revision in the future
establishing inter-pollutant offset ratios
supported by an appropriate
demonstration, or alternatively revise
these ratios in accordance with the July
21, 2011, EPA memorandum that
addresses the Federal inter-pollutant
offset policy (76 FR 80747). The EPA
proposes to approve and IBR the
revisions to OAR 340–225–0090, except
for OAR 340–225–0090(2)(a)(C), and the
revision to 340–225–0090(2)(a)(B) based
on the PM2.5 inter-pollutant offset ratio,
as it provides equivalent protection of
the NAAQS and encourages improved
air quality by reducing direct PM
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emissions from wood fired devices in
the Klamath Falls NAA.
Division 240: Rules for Areas With
Unique Air Quality Needs
Revisions to OAR 340–240–0110,
340–240–0030, 340–240–0500, 340–
240–0510, 340–240–0520, 340–240–
0530, 340–240–0540, 340–240–0550,
340–240–0560, describe and allow for
the implementation of multiple control
measures associated with emissions of
PM2.5 in the Klamath Falls NAA. The
ODEQ updated the rule definitions to
include necessary cross-references to
applicable rules and to add new
definitions needed for implementation
of the control measures. Control
measures include opacity standards,
fugitive emissions control, operation
and maintenance plan requirements,
industrial source compliance schedules,
and residential wood fuel-fired device
offset requirements for new sources, and
PM2.5 and PM10 offsets.
The 20% opacity standard and
fugitive emissions control rules limit
emissions being emitted into the
Klamath Falls NAA from stationary
sources including industrial facilities.
The operation and maintenance plan
requirements and the industrial source
compliance schedule (a schedule to
develop and implement a plan for
compliance with the opacity standards,
fugitive emissions requirements, and
operations and maintenance plans listed
in OAR 340–240–0510 through –0540),
support reduced particulate matter
emissions through enhanced
management of source operation. The
offsets rules in OAR 340–240–0550, in
coordination with the rule revisions in
OAR Chapter 340, Division 225, allow
for offsets to be obtained within the
Klamath Falls NAA from residential
wood combustion at a ratio of one ton
of PM2.5 emissions to one ton of
woodstove emissions reductions while
ensuring that the increased emissions
from new or modified sources will not
cause or contribute to a violation of the
NAAQS. The EPA proposes to approve
these rules as they are permanent and
enforceable SIP strengthening measures
that contribute to progress toward
attainment of the 2006 PM2.5 24-hr
NAAQS in this area.
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Division 264: Rules for Open Burning
The revisions to OAR Chapter 340,
Division 264 enhance the open burning
rule in Oregon and the Klamath Falls
NAA. Specifically, the revised rule
includes language aligning open
burning with ideal dispersion
conditions; provides a description and
map of the Klamath Basin Open Burning
Control Area; and provides rules
specific to the Klamath Falls NAA
prohibiting open burning from
industrial, commercial, construction
and demolition operations. The rule
revisions will reduce emissions through
the prohibition of open burning within
the Klamath Falls NAA. The EPA
proposes to approve and IBR these rule
revisions because they are permanent
and enforceable measures that support
attainment and maintenance of the
NAAQS by reducing the amount of
particulate matter in the area.
tkelley on DSK3SPTVN1PROD with PROPOSALS
Klamath County Clean Air Ordinances
In its December 12, 2012 submittal,
the ODEQ included as control measures
the 2007 and 2012 Klamath County
Clean Air Ordinances. These two
ordinances establish permanent and
enforceable control measures on sources
that account for the majority of PM2.5
emissions in the Klamath Falls NAA.
The 2007 Klamath County Clean Air
Ordinance is more specifically
identified as Chapter 406, Ordinance
No. 63.05, enacted August 7, 2007 (2007
Ordinance). The 2012 Klamath County
Clean Air Ordinance is more
specifically identified as Chapter 406,
Ordinance No. 63.06, enacted December
31, 2012 (2012 Ordinance).
The 2007 and 2012 Ordinances were
enacted to control emissions from home
heating devices for the purpose of
meeting the 2006 PM2.5 24-hr NAAQS.
The 2007 ordinance provides for lower
thresholds for yellow and red air quality
advisory days which require the
curtailment of wood burning and
therefore reduce emissions of PM2.5 and
PM2.5 precursors. With these lower
thresholds, wood burning restrictions
would be in place on days that most
likely contribute to a 24-hour NAAQS
violation. This provision, in conjunction
with increased enforcement at the
County level, is expected to be a core
part of the area’s attainment plan. The
2007 ordinance has provisions identical
to the state wide Heat Smart Program
that require removal of uncertified
stoves upon sale of a home, and also
provisions that reduce the number of
available residential open burning days
and prohibit the use of burn barrels. The
2012 ordinance required new and
VerDate Sep<11>2014
17:03 Dec 29, 2014
Jkt 235001
retrofit fireplaces to meet lower
emissions standards.
The EPA proposes to approve and IBR
the 2007 and 2012 Klamath Falls Clean
Air Ordinances because they support
attainment and maintenance of the
NAAQS in the Klamath Falls NAA.
III. Proposed Action
The EPA proposes to approve the
PM2.5 and PM2.5 precursor emissions
inventory for the Klamath Falls NAA,
submitted by ODEQ on December 12,
2012, as meeting the emissions
inventory requirements of section
172(c)(3) of the CAA for 2006 PM2.5 24hr NAAQS nonattainment area
planning. The EPA also proposes to
approve and incorporate into the SIP the
specific control measures submitted by
the ODEQ on December 12, 2012, to the
extent set forth in this notice. These
control measures are described in this
action and are included in the docket
for this proposed action. If approved,
these specific control measures would
become part of the Oregon SIP. The EPA
is not taking action on certain aspects of
the revisions submitted by the ODEQ.
The EPA expects to take action on the
remaining SIP revisions and any
additional revisions that may be
submitted by the ODEQ in the future.
IV. Statutory and Executive Order
Reviews
Under the CAA, the Administrator is
required to approve a SIP submission
that complies with the provisions of the
CAA and applicable federal regulations.
42 U.S.C. 7410(k); 40 CFR 52.02(a).
Thus, in reviewing SIP submissions, the
EPA’s role is to approve state choices,
provided that they meet the criteria of
the CAA. Accordingly, this action
merely proposes to approve state law as
meeting federal requirements and does
not impose additional requirements
beyond those imposed by State law. For
that reason, this proposed action:
• Is not a ‘‘significant regulatory
action’’ subject to review by the Office
of Management and Budget under
Executive Order 12866 (58 FR 51735,
October 4, 1993);
• Does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act (44
U.S.C. 3501 et seq.);
• Is certified as not having a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act (5
U.S.C. 601 et seq.);
• Does not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
in the Unfunded Mandates Reform Act
of 1995 (Pub. L. 104–4);
PO 00000
Frm 00063
Fmt 4702
Sfmt 4702
• Does not have federalism
implications as specified in Executive
Order 13132 (64 FR 43255, August 10,
1999);
• Is not an economically significant
regulatory action based on health or
safety risks subject to Executive Order
13045 (62 FR 19885, April 23, 1997);
• Is not a significant regulatory action
subject to Executive Order 13211 (66 FR
28355, May 22, 2001);
• Is not subject to requirements of
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (15 U.S.C. 272 note) because
application of those requirements would
be inconsistent with the CAA; and
• Does not provide the EPA with the
discretionary authority to address, as
appropriate, disproportionate human
health or environmental effects, using
practicable and legally permissible
methods, under Executive Order 12898
(59 FR 7629, February 16, 1994).
In addition, this SIP is not approved to
apply on any Indian reservation land or
in any other area where EPA or an
Indian tribe has demonstrated that a
tribe has jurisdiction. In those areas of
Indian country, the rule does not have
tribal implications as specified by
Executive Order 13175 (65 FR 67249,
November 9, 2000), nor will it impose
substantial direct costs on tribal
governments or preempt tribal law.
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Nitrogen dioxide,
Incorporation by reference, Particulate
matter, Reporting and recordkeeping
requirements, Sulfur oxides, Volatile
organic compounds.
Authority: 42 U.S.C. 7401 et seq.
Dated: December 3, 2014.
Dennis J. McLerran,
Regional Administrator, Region 10.
[FR Doc. 2014–30498 Filed 12–29–14; 8:45 am]
BILLING CODE 6560–50–P
DEPARTMENT OF HEALTH AND
HUMAN SERVICES
Office of Inspector General
42 CFR Part 1001
Solicitation of New Safe Harbors and
Special Fraud Alerts
Office of Inspector General
(OIG), HHS.
ACTION: Notice of intent to develop
regulations.
AGENCY:
In accordance with section
205 of the Health Insurance Portability
SUMMARY:
E:\FR\FM\30DEP1.SGM
30DEP1
Agencies
[Federal Register Volume 79, Number 249 (Tuesday, December 30, 2014)]
[Proposed Rules]
[Pages 78372-78376]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2014-30498]
=======================================================================
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R10-OAR-2013-0005; FRL-9920-97-Region 10]
Approval and Promulgation of Implementation Plans; Klamath Falls,
Oregon Nonattainment Area; Fine Particulate Matter Emissions Inventory
and SIP Strengthening Measures
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: The Oregon Department of Environmental Quality (ODEQ)
submitted a revision to the State Implementation Plan (SIP), dated
December 14, 2012, to address Clean Air Act (CAA or the Act)
requirements for the Klamath Falls, Oregon nonattainment area for the
2006 24-hour fine particulate matter (PM2.5) national
ambient air quality standard (NAAQS). The EPA proposes to approve the
emissions inventory contained in the ODEQ's submittal as meeting the
requirement to submit a comprehensive, accurate, and current inventory
of direct PM2.5 and PM2.5 precursor emissions in
Klamath Falls, Oregon. The EPA also proposes to approve
PM2.5 control measures contained in the December 2012
submittal because incorporation of these measures will strengthen the
Oregon SIP and reduce sources of PM2.5 emissions in the
Klamath Falls, Oregon nonattainment area (Klamath Falls NAA) that
contribute to violations of the 2006 PM2.5 NAAQS.
DATES: Comments must be received on or before January 29, 2015.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-R10-
OAR-2013-0005, by any of the following methods:
www.regulations.gov: Follow the on-line instructions for
submitting comments.
Email: R10-Public_Comments@epa.gov.
Mail: Justin A. Spenillo, EPA Region 10, Office of Air,
Waste and Toxics (AWT-150), 1200 Sixth Avenue, Suite 900, Seattle, WA
98101.
Hand Delivery/Courier: EPA Region 10, 1200 Sixth Avenue,
Suite 900, Seattle, WA 98101. Attention: Justin A. Spenillo, Office of
Air, Waste and Toxics, AWT-150. Such deliveries are only accepted
during normal hours of operation, and special arrangements should be
made for deliveries of boxed information
Instructions: Direct your comments to Docket ID No. EPA-R10-OAR-
2013-0005. The EPA's policy is that all comments received will be
included in the public docket without change and may be made available
online at www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
Confidential Business Information (CBI) or other information the
disclosure of which is restricted by statute. Do not submit information
that you consider to be CBI or otherwise protected through
www.regulations.gov or email. The www.regulations.gov Web site is an
``anonymous access'' system, which means the EPA will not know your
identity or contact information unless you provide it in the body of
your comment. If you send an email comment directly to the EPA without
going through www.regulations.gov your email address will be
automatically captured and included as part of the comment that is
placed in the public docket and made available on the Internet. If you
submit an electronic comment, the EPA recommends that you include your
name and other contact information in the body of your comment and with
any disk or CD-ROM you submit. If the EPA cannot read your comment due
to technical difficulties and cannot contact you for clarification, the
EPA may not be able to consider your comment. Electronic files should
avoid the use of special characters, any form of encryption, and be
free of any defects or viruses.
Docket: All documents in the docket are listed in the
www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information,
the disclosure of which is restricted by statute. Certain other
material, such as copyrighted material, is not placed on the Internet
and will be publicly available only in hard copy. Publicly available
docket materials are available either electronically in
www.regulations.gov or in hard copy during normal business hours at the
Office of Air, Waste and Toxics, EPA Region 10, 1200 Sixth Avenue,
Seattle WA, 98101.
FOR FURTHER INFORMATION CONTACT: Justin A. Spenillo at (206) 553-6125,
spenillo.justin@epa.gov, or the above EPA, Region 10 address.
SUPPLEMENTARY INFORMATION: Throughout this document whenever ``we,''
``us,'' or ``our'' is used, we mean the EPA.
Table of Contents
I. Background
A. PM2.5 National Ambient Air Quality Standards
B. Designation of PM2.5 Nonattainment Areas
C. Submittal Requirements for PM2.5 Nonattainment
Areas
II. Analysis of the State's Submittal
A. Emissions Inventory
B. Description of the Klamath County PM2.5 Control
Measures
III. Proposed Action
IV. Statutory and Executive Order Reviews
I. Background
A. PM2.5 National Ambient Air Quality Standards
Under section 109 of the CAA, the EPA establishes NAAQS for certain
pervasive air pollutants (referred to as ``criteria pollutants'') and
conducts periodic reviews of the NAAQS to determine whether they should
be revised or whether new NAAQS should be established. After a new
NAAQS is established or an existing NAAQS is revised, all areas across
the country are evaluated to determine whether they meet the new or
revised standard, and
[[Page 78373]]
area designations are promulgated based on that evaluation.
On July 18, 1997, the EPA revised the NAAQS for particulate matter
to add new standards for fine particles, using PM2.5
(particles less than or equal to 2.5 micrometers in aerodynamic
diameter) as the indicator for the pollutant. The EPA established
primary and secondary \1\ annual and 24-hour standards for
PM2.5 (62 FR 38652). The annual standard was set at 15.0
micrograms per cubic meter ([mu]g/m\3\), based on a 3-year average of
the annual mean PM2.5 concentrations, and the 24-hour
standard was set at 65 [mu]g/m\3\, based on the 3-year average of the
98th percentile of 24-hour PM2.5 concentrations. On October
17, 2006, the EPA revised the level of the 24-hour PM2.5
NAAQS to 35 [mu]g/m\3\, based on a 3-year average of the 98th
percentile of 24-hour concentrations (71 FR 61144). On December 14,
2012, the EPA revised the primary annual PM2.5 NAAQS to
provide increased protection of public health and welfare from fine
particle pollution (78 FR 3086, January 15, 2013). In that action, the
EPA revised the primary annual PM2.5 standard, strengthening
it from 15.0 micrograms per cubic meter ([mu]g/m\3\) to 12.0 [mu]g/
m\3\, which is attained when the 3-year average of the annual
arithmetic means does not exceed 12.0 [mu]g/m\3\.
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\1\ For a given air pollutant, ``primary'' national ambient air
quality standards are those determined by the EPA as requisite to
protect the public health, and ``secondary'' standards are those
determined by the EPA as requisite to protect the public welfare
from any known or anticipated adverse effects associated with the
presence of such air pollutant in the ambient air. See CAA section
109(b).
---------------------------------------------------------------------------
B. Designation of PM2.5 Nonattainment Areas
Effective December 14, 2009, the EPA established the initial air
quality designations for most areas in the United States for the 2006
24-hour PM2.5 NAAQS (74 FR 58688, November 13, 2009). The
Klamath Falls area was designated nonattainment for the 2006 24-hour
PM2.5 NAAQS. The boundaries for this area are described in
40 CFR 81.338.
C. Submittal Requirements for PM2.5 Nonattainment Areas
In March 2012, the EPA issued guidance to states for implementation
of the 2006 PM2.5 NAAQS (March 2012 Implementation
Guidance).\2\ The guidance recommended that states make submissions for
the 2006 PM2.5 NAAQS consistent with the substantive
requirements developed for implementation of the 1997 PM2.5
NAAQS at 40 CFR part 51, subpart Z (Provisions for Implementation of
PM2.5 National Ambient Air Quality Standards, 40 CFR
51.1000, et seq.). In December 2012, based on the March 2012
Implementation Guidance, the ODEQ submitted a SIP revision intended to
address the nonattainment planning requirements for the Klamath Falls
NAA.
---------------------------------------------------------------------------
\2\ Memorandum from Stephen D. Page, Implementation Guidance for
the 2006 24-Hour Fine Particulate (PM2.5) National
Ambient Air Quality Standards (Mar. 2, 2012).
---------------------------------------------------------------------------
On January 4, 2013, the Court of Appeals for the District of
Columbia remanded to the EPA the Clean Air Fine Particle Implementation
Rule (72 FR 20586, Apr. 25, 2007) (hereafter referred to as the
``PM2.5 implementation rule'') which formed the basis of the
40 CFR part 51, subpart Z nonattainment planning requirements. Natural
Resources Defense Council v. EPA, 706 F.3d 428 (D.C. Cir. 2013). The
Court concluded that the EPA had improperly based the PM2.5
implementation rule solely upon the requirements of part D, subpart 1
of the CAA, and had failed to address the requirements of part D,
subpart 4. As a result of the Court's remand of the PM2.5
implementation rule, the EPA withdrew its March 2012 Implementation
Guidance because it was based largely on the remanded rule promulgated
to implement the 1997 PM2.5 NAAQS.\3\ The EPA is currently
engaged in rulemaking to address the Court's remand of the
PM2.5 implementation rule. In the interim, however, the EPA
continues to take action on SIP submissions from states intended to
address nonattainment planning requirements for the 2006
PM2.5 NAAQS, consistent with the CAA.
---------------------------------------------------------------------------
\3\ Memorandum from Stephen D. Page, Withdrawal of
Implementation Guidance for the 2006 24-Hour Fine Particle
(PM2.5) National Ambient Air Quality Standards (Jun. 6,
2013).
---------------------------------------------------------------------------
This action is limited to proposing approval of the emissions
inventory of direct PM2.5 and PM2.5 precursors
submitted by the ODEQ for the Klamath Falls NAA as required under
section 172(c)(3) of the CAA, and the approval of specific control
measures that are expected to strengthen the SIP. These control
measures independently meet requirements for control measures in
attainment plans and the emissions reductions they achieve will
contribute to attainment of the 2006 PM2.5 NAAQS in the
Klamath Falls NAA.
II. Analysis of the State's Submittal
A. Emissions Inventory
The EPA promulgated emissions inventory requirements for the 1997
PM2.5 NAAQS as part of the PM2.5 implementation
rule at 40 CFR 51.1008. The decision in NRDC v. EPA remanded the
PM2.5 implementation rule because it did not incorporate the
specific particulate matter requirements of subpart 4, part D, title I.
The emission inventory requirements set forth in the PM2.5
implementation rule were based on the CAA section 172(c)(3)
requirements in subpart 1. Subpart 4 contains no specific provision
governing emissions inventories for PM10 or PM2.5
nonattainment areas that supersedes the general emissions inventory
requirement for all nonattainment areas in section 172(c)(3). See
``State Implementation Plans; General Preamble for the Implementation
of Title I of the Clean Air Act Amendments of 1990,'' (57 FR 13498,
13539, April 16, 1992) (hereinafter ``General Preamble''). Accordingly,
the EPA is evaluating the ODEQ's emissions inventory for the Klamath
Falls NAA pursuant to the CAA requirements in section 172(c)(3).
Section 172(c)(3) of the CAA requires a state with an area
designated as nonattainment to submit to the EPA for approval a
comprehensive, accurate, and current inventory of actual emissions of
the pollutant at issue, including emissions of any precursor of that
pollutant, for the nonattainment area. These inventories provide a
detailed accounting of all emissions and emissions sources by pollutant
and precursor pollutant within the nonattainment area. In addition,
inventories are used to model air quality to demonstrate attainment of
the 2006 PM2.5 NAAQS as expeditiously as practicable. The
EPA reviewed, in accordance with the August 2005 EPA guidance,
``Emissions Inventory Guidance for Implementation of Ozone and
Particulate Matter NAAQS and Regional Haze Regulations,'' the
procedures and methodologies used by the ODEQ to develop the emission
inventory for the 2008 base year emissions inventory for the Klamath
Falls NAA. In accordance with section 172(c)(3) and consistent with EPA
guidance, Oregon's attainment plan as described below includes a
comprehensive, accurate, and current inventory of emissions of all
direct PM2.5 and PM2.5 precursors in the Klamath
Falls NAA.
To develop an emissions inventory that matches the conditions under
which the design value concentration are measured, the ODEQ emissions
inventory addresses annual emissions, typical season day emissions, and
worst case day emissions. Annual emissions, measured in tons per year
(``tpy''), are the total amount of emissions over the course of a
calendar year. The typical season day and worst-case day
[[Page 78374]]
emissions are measured in pounds (lbs) per day and are calculated for
the PM season, which is the four-month period between November and
February when ambient PM concentrations from anthropogenic sources are
generally the highest. Typical season day emissions are the average
emissions over the four-month PM season, and worst case day emissions
are the amount emitted on winter days with a diurnal temperature range
representative of PM2.5 exceedances. Most source categories
are modeled using the typical season day emissions. Worst-case day
emissions are better suited for select sources, such as residential
wood combustion and motor vehicles, with emissions highly dependent on
temperature. At colder temperatures there is a behavioral increase in
home heating using woodstoves, and vehicle emissions associated with
start-up emissions are higher on colder days.
The year 2008 was selected by ODEQ as the base year for the
emissions inventory because it was the most recent year that Oregon
completed the NEI data submittal prior to the designation of the
Klamath Falls NAA in 2009. The selection of 2008 as the baseline year
for the emissions inventory is consistent with the emissions inventory
requirement in section 172(c)(3) because it provides an inventory of
emissions for one of the years relied upon for the nonattainment
designation. The ODEQ's 2008 base year emissions inventory includes
emissions of direct PM2.5 and PM2.5 precursors
that cover the general source categories of stationary point sources,
stationary nonpoint sources (area sources), non-road mobile sources,
and on-road mobile sources. The main sources of emissions in the
Klamath Falls NAA are residential wood combustion, mobile and non-road
sources, and point sources. The pollutants that comprise the 2008 base
year inventory include direct PM2.5 and the precursors to
the formation of PM2.5 which are nitrogen oxide
(NOX), volatile organic compounds (VOCs), ammonia
(NH3), and sulfur dioxide (SO2).
The point source inventory provides facility-specific data for
point source emissions from Klamath Falls' permitted stationary
sources. Permitted point sources include industrial sources, non-
industrial sources, gas stations, crematories, and portable sources.
The emissions inventory includes actual point source emissions for both
the annual and the seasonal inventory. For purposes of the worst-case
day emission inventory, the emissions for permitted point sources are
reported at 80% of the permitted operating capacity because such
specific daily actual emissions are not available for permitted point
sources in the same manner as annual and typical season emissions. The
EPA agrees that 80% of permitted emissions is a conservative estimate
for worst-case day actual emissions and, given that permitted point
sources were not found to be significantly contributing to the
monitored violations. This will be further discussed in a future notice
when the EPA acts on the ODEQ's control strategy for the Klamath Falls
NAA.
The complete inventory, located in the docket for this rulemaking,
also includes a description of minor non-permitted point sources. Area
sources for the Klamath Falls NAA are divided into six groups: Waste
disposal, treatment and recovery; small stationary fossil fuel
combustion; residential wood combustion; fugitive dust; evaporative/
off-gassing emissions sources; and miscellaneous area sources. The on-
road mobile source emissions inventory includes all sources of mobile
exhaust, brake, and tire emissions generated by passenger vehicles,
trucks, miscellaneous vehicles, and re-entrained road dust. Non-road
mobile sources inventoried include aircraft, gasoline and diesel-
powered vehicles and equipment, recreational marine vessels, and
trains.
The ODEQ compiled the emissions inventory relying on information
from a variety of sources. Permitted point source emissions data were
taken from the ODEQ Tracking Reporting and Administration of Air
Contaminant Sources (TRAACS) database which is submitted to the EPA
National Emissions Inventory System. Many area source emissions were
taken from the 2008 EPA National Emissions Inventory (NEI) v.1.5. The
ODEQ Area Mobile Emissions Estimates (AMEE) database was also a source
of emissions data for mobile emissions. Additional emissions
information was taken from a 2007/2008 residential wood combustion
survey and from use of the EPA Motor Vehicle Emission Simulator
(MOVES). All remaining emissions were modeled or inventoried
specifically for this attainment plan. The full emissions inventory
submitted by the ODEQ and a detailed description of the methodology
used to compile the inventory is presented in Attachment 3.3l of the
SIP submittal included in the docket for this action.
Table 1 summarizes the annual emissions for Klamath Falls in 2008
and Table 2 summarizes the worst-case day emissions for Klamath Falls
in 2008. Typical season day emissions information can be found in
Attachment 3.3l of the SIP submittal included in the docket for this
action.
Table 1--2008 Klamath Falls, Annual Emissions
[tpy]
----------------------------------------------------------------------------------------------------------------
Source sector PM2.5 SOX NOX NH3 VOC
----------------------------------------------------------------------------------------------------------------
Point........................... 143.4 47.8 329.3 70.4 997.2
Area............................ 403.0 49.1 114.3 161.9 972.9
Onroad.......................... 92.2 6.4 1,431.6 11.4 694.2
Nonroad......................... 16.1 6.6 360.9 .............. 246.0
-------------------------------------------------------------------------------
Total....................... 654.7 109.9 2,236.1 243.7 2,910.4
----------------------------------------------------------------------------------------------------------------
Table 2--2008 Klamath Falls, Worst-Case Day
[lbs/day]
----------------------------------------------------------------------------------------------------------------
Source sector PM2.5 SOX NOX NH3 VOC
----------------------------------------------------------------------------------------------------------------
Point........................... 1,517 357 3,247 1,453 10,301
Area............................ 2,851 546 1,391 772 6,483
Onroad.......................... 917 36 7,990 62 4,734
[[Page 78375]]
Nonroad......................... 135 108 2,855 .............. 876
rrrrrrrrrrrrrrrrrrrrrrrrrrrrrrrrr
Total....................... 5,420 1,046 15,483 2,287 22,754
----------------------------------------------------------------------------------------------------------------
The EPA reviewed the results, procedures and methodologies for the
2008 base year emissions inventory in accordance with the EPA's current
guidance, ``Emissions Inventory Guidance for Implementation of Ozone
and Particulate Matter NAAQS and Regional Haze Regulations'' (August
2005). The ODEQ used standard procedures to develop the emissions
inventory and appropriately used seasonal and worst-case day emissions
inventories to represent episodic meteorological conditions when
PM2.5 levels are of the greatest concern. For this reason,
the EPA is proposing approval of Klamath Falls' 2008 base year
emissions inventory as meeting the requirements of section 172(c)(3) of
the CAA.
B. Description of the Klamath County PM2.5 Control Measures
On December 12, 2012, the ODEQ submitted to the EPA for approval
revisions to a number of rules related to the Klamath Falls NAA. These
revisions consist of updates to identify the Klamath Falls NAA and to
adopt local and state measures to ensure permanent and enforceable
control strategies intended to bring the area back into attainment
through control of PM2.5 and its precursors. Specifically,
the ODEQ revised rules in Oregon Administrative Rules (OAR) Chapter
340, Divisions 200, 204, 225, 240, 262, and 264. These revisions, and
the EPA's proposed actions on them, are described below.
Division 204: Designation of Air Quality Areas
The ODEQ revised OAR Chapter 340, Division 204 to include a
description of the Klamath Falls PM2.5 NAA boundary. The EPA
proposes to approve and incorporate by reference (IBR) this revision
into the SIP because the area description is essential for delineating
the nonattainment area, and we believe the area description is
consistent with the EPA description in the designation for the area.
Division 225: Air Quality Analysis Requirements
The ODEQ revised OAR 340-225-0090, in conjunction with promulgating
OAR 340-240-0550, as encouragement for direct PM10 and
PM2.5 emissions reductions from residential wood-fired
devices as a means to offset, in an equal or greater amount, emissions
increases from new major sources or major modifications to major
sources located in the Klamath Falls NAA, provided such sources do not
cause or contribute to a violation of the NAAQS. The revisions to OAR
340-225-0090 exempt a source which proposes to use qualifying woodstove
offsets from the need to conduct an air dispersion modeling analysis to
demonstrate a net air quality benefit as would otherwise be required.
Woodstove emissions are the primary source of PM2.5
emissions contributing to NAAQS violations in the NAA and reductions in
woodstove emissions would presumptively result in a net air quality
benefit when used to offset new emissions from a stationary source
located within the NAA. A source proposing to use other sources of
emission offsets, or woodstove offsets that don't meet the requirements
of OAR 340-240-0550, would still need to conduct a dispersion modeling
analysis to demonstrate a net air quality benefit. The revisions are
designed to maintain and promote continued air quality improvement
while allowing for economic growth that does not negatively affect the
airshed.
In a letter dated September 15, 2014, Oregon withdrew the submitted
SIP revision for OAR 340-225-0090(2)(a)(C). Accordingly, the EPA is not
acting on the revisions to OAR 340-225-0090(2)(a)(C) which establish
inter-pollutant offset ratios. Oregon may submit a revision in the
future establishing inter-pollutant offset ratios supported by an
appropriate demonstration, or alternatively revise these ratios in
accordance with the July 21, 2011, EPA memorandum that addresses the
Federal inter-pollutant offset policy (76 FR 80747). The EPA proposes
to approve and IBR the revisions to OAR 340-225-0090, except for OAR
340-225-0090(2)(a)(C), and the revision to 340-225-0090(2)(a)(B) based
on the PM2.5 inter-pollutant offset ratio, as it provides
equivalent protection of the NAAQS and encourages improved air quality
by reducing direct PM emissions from wood fired devices in the Klamath
Falls NAA.
Division 240: Rules for Areas With Unique Air Quality Needs
Revisions to OAR 340-240-0110, 340-240-0030, 340-240-0500, 340-240-
0510, 340-240-0520, 340-240-0530, 340-240-0540, 340-240-0550, 340-240-
0560, describe and allow for the implementation of multiple control
measures associated with emissions of PM2.5 in the Klamath
Falls NAA. The ODEQ updated the rule definitions to include necessary
cross-references to applicable rules and to add new definitions needed
for implementation of the control measures. Control measures include
opacity standards, fugitive emissions control, operation and
maintenance plan requirements, industrial source compliance schedules,
and residential wood fuel-fired device offset requirements for new
sources, and PM2.5 and PM10 offsets.
The 20% opacity standard and fugitive emissions control rules limit
emissions being emitted into the Klamath Falls NAA from stationary
sources including industrial facilities. The operation and maintenance
plan requirements and the industrial source compliance schedule (a
schedule to develop and implement a plan for compliance with the
opacity standards, fugitive emissions requirements, and operations and
maintenance plans listed in OAR 340-240-0510 through -0540), support
reduced particulate matter emissions through enhanced management of
source operation. The offsets rules in OAR 340-240-0550, in
coordination with the rule revisions in OAR Chapter 340, Division 225,
allow for offsets to be obtained within the Klamath Falls NAA from
residential wood combustion at a ratio of one ton of PM2.5
emissions to one ton of woodstove emissions reductions while ensuring
that the increased emissions from new or modified sources will not
cause or contribute to a violation of the NAAQS. The EPA proposes to
approve these rules as they are permanent and enforceable SIP
strengthening measures that contribute to progress toward attainment of
the 2006 PM2.5 24-hr NAAQS in this area.
[[Page 78376]]
Division 264: Rules for Open Burning
The revisions to OAR Chapter 340, Division 264 enhance the open
burning rule in Oregon and the Klamath Falls NAA. Specifically, the
revised rule includes language aligning open burning with ideal
dispersion conditions; provides a description and map of the Klamath
Basin Open Burning Control Area; and provides rules specific to the
Klamath Falls NAA prohibiting open burning from industrial, commercial,
construction and demolition operations. The rule revisions will reduce
emissions through the prohibition of open burning within the Klamath
Falls NAA. The EPA proposes to approve and IBR these rule revisions
because they are permanent and enforceable measures that support
attainment and maintenance of the NAAQS by reducing the amount of
particulate matter in the area.
Klamath County Clean Air Ordinances
In its December 12, 2012 submittal, the ODEQ included as control
measures the 2007 and 2012 Klamath County Clean Air Ordinances. These
two ordinances establish permanent and enforceable control measures on
sources that account for the majority of PM2.5 emissions in
the Klamath Falls NAA. The 2007 Klamath County Clean Air Ordinance is
more specifically identified as Chapter 406, Ordinance No. 63.05,
enacted August 7, 2007 (2007 Ordinance). The 2012 Klamath County Clean
Air Ordinance is more specifically identified as Chapter 406, Ordinance
No. 63.06, enacted December 31, 2012 (2012 Ordinance).
The 2007 and 2012 Ordinances were enacted to control emissions from
home heating devices for the purpose of meeting the 2006
PM2.5 24-hr NAAQS. The 2007 ordinance provides for lower
thresholds for yellow and red air quality advisory days which require
the curtailment of wood burning and therefore reduce emissions of
PM2.5 and PM2.5 precursors. With these lower
thresholds, wood burning restrictions would be in place on days that
most likely contribute to a 24-hour NAAQS violation. This provision, in
conjunction with increased enforcement at the County level, is expected
to be a core part of the area's attainment plan. The 2007 ordinance has
provisions identical to the state wide Heat Smart Program that require
removal of uncertified stoves upon sale of a home, and also provisions
that reduce the number of available residential open burning days and
prohibit the use of burn barrels. The 2012 ordinance required new and
retrofit fireplaces to meet lower emissions standards.
The EPA proposes to approve and IBR the 2007 and 2012 Klamath Falls
Clean Air Ordinances because they support attainment and maintenance of
the NAAQS in the Klamath Falls NAA.
III. Proposed Action
The EPA proposes to approve the PM2.5 and
PM2.5 precursor emissions inventory for the Klamath Falls
NAA, submitted by ODEQ on December 12, 2012, as meeting the emissions
inventory requirements of section 172(c)(3) of the CAA for 2006
PM2.5 24-hr NAAQS nonattainment area planning. The EPA also
proposes to approve and incorporate into the SIP the specific control
measures submitted by the ODEQ on December 12, 2012, to the extent set
forth in this notice. These control measures are described in this
action and are included in the docket for this proposed action. If
approved, these specific control measures would become part of the
Oregon SIP. The EPA is not taking action on certain aspects of the
revisions submitted by the ODEQ. The EPA expects to take action on the
remaining SIP revisions and any additional revisions that may be
submitted by the ODEQ in the future.
IV. Statutory and Executive Order Reviews
Under the CAA, the Administrator is required to approve a SIP
submission that complies with the provisions of the CAA and applicable
federal regulations. 42 U.S.C. 7410(k); 40 CFR 52.02(a). Thus, in
reviewing SIP submissions, the EPA's role is to approve state choices,
provided that they meet the criteria of the CAA. Accordingly, this
action merely proposes to approve state law as meeting federal
requirements and does not impose additional requirements beyond those
imposed by State law. For that reason, this proposed action:
Is not a ``significant regulatory action'' subject to
review by the Office of Management and Budget under Executive Order
12866 (58 FR 51735, October 4, 1993);
Does not impose an information collection burden under the
provisions of the Paperwork Reduction Act (44 U.S.C. 3501 et seq.);
Is certified as not having a significant economic impact
on a substantial number of small entities under the Regulatory
Flexibility Act (5 U.S.C. 601 et seq.);
Does not contain any unfunded mandate or significantly or
uniquely affect small governments, as described in the Unfunded
Mandates Reform Act of 1995 (Pub. L. 104-4);
Does not have federalism implications as specified in
Executive Order 13132 (64 FR 43255, August 10, 1999);
Is not an economically significant regulatory action based
on health or safety risks subject to Executive Order 13045 (62 FR
19885, April 23, 1997);
Is not a significant regulatory action subject to
Executive Order 13211 (66 FR 28355, May 22, 2001);
Is not subject to requirements of Section 12(d) of the
National Technology Transfer and Advancement Act of 1995 (15 U.S.C. 272
note) because application of those requirements would be inconsistent
with the CAA; and
Does not provide the EPA with the discretionary authority
to address, as appropriate, disproportionate human health or
environmental effects, using practicable and legally permissible
methods, under Executive Order 12898 (59 FR 7629, February 16, 1994).
In addition, this SIP is not approved to apply on any Indian
reservation land or in any other area where EPA or an Indian tribe has
demonstrated that a tribe has jurisdiction. In those areas of Indian
country, the rule does not have tribal implications as specified by
Executive Order 13175 (65 FR 67249, November 9, 2000), nor will it
impose substantial direct costs on tribal governments or preempt tribal
law.
List of Subjects in 40 CFR Part 52
Environmental protection, Air pollution control, Nitrogen dioxide,
Incorporation by reference, Particulate matter, Reporting and
recordkeeping requirements, Sulfur oxides, Volatile organic compounds.
Authority: 42 U.S.C. 7401 et seq.
Dated: December 3, 2014.
Dennis J. McLerran,
Regional Administrator, Region 10.
[FR Doc. 2014-30498 Filed 12-29-14; 8:45 am]
BILLING CODE 6560-50-P