Official Release of EMFAC2011 Motor Vehicle Emission Factor Model for Use in the State of California, 14533-14536 [2013-05245]
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Federal Register / Vol. 78, No. 44 / Wednesday, March 6, 2013 / Notices
ENVIRONMENTAL PROTECTION
AGENCY
[EPA–R09–OAR–2013–0126; FRL–9788–3]
Official Release of EMFAC2011 Motor
Vehicle Emission Factor Model for Use
in the State of California
Environmental Protection
Agency (EPA).
ACTION: Notice of Availability.
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AGENCY:
SUMMARY: EPA is approving and
announcing the availability of the latest
version of the California EMFAC model
(short for EMission FACtor) for use in
state implementation plan (SIP)
development and transportation
conformity in California. EMFAC2011 is
the latest update to the EMFAC model
for use by California state and local
governments to meet Clean Air Act
(CAA) requirements. The new model,
which is based on new and improved
data, calculates air pollution emissions
factors for passenger cars, trucks,
motorcycles, motor homes and buses.
Today’s notice also sets the date after
which EMFAC2011 is required to be
used statewide in all new regional
emissions analyses and carbon
monoxide (CO), particulate matter of ten
microns or less (PM10) and fine
particulate matter (PM2.5) hot-spot
analyses for transportation conformity
determinations in California. Since the
EMFAC model is used only in
California, EPA’s approval of the model
does not affect MOVES model users in
other states.
DATES: EPA’s approval of the
EMFAC2011 emissions model for SIP
and conformity purposes is effective
March 6, 2013. EMFAC2011 must be
used for all new regional emissions
analyses and CO, PM10 and PM2.5 hotspot analyses that are started on or after
September 6, 2013.
FOR FURTHER INFORMATION CONTACT:
Karina O’Connor,
oconnor.karina@epa.gov, (775) 433–
8176, Air Planning Office (AIR–2), Air
Division, U.S. EPA, Region 9, 75
Hawthorne Street, San Francisco,
California, 94105–3901.
SUPPLEMENTARY INFORMATION: Copies of
the official version of the EMFAC2011
model are available on the California
Air Resources Board (CARB) Web site:
https://www.arb.ca.gov/msei/
modeling.htm (model, technical support
documents, etc.).
I. Background
A. What is the EMFAC model?
The EMFAC model is a computer
model that can estimate emission rates
for on-road mobile sources (‘‘motor
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vehicles’’) for calendar years from 1990
to 2035 operating in California.
Pollutant emissions for hydrocarbons
(HC), CO, nitrogen oxides (NOX), PM10,
PM2.5, lead, carbon dioxide (CO2), and
sulfur oxides are output from the model.
Emissions are calculated for forty-two
different vehicle classes composed of
passenger cars, various types of trucks
and buses, motorcycles, and motor
homes.
EMFAC is used to calculate current
and future inventories of motor vehicle
emissions at the state, air district, air
basin, or county level. EMFAC contains
default vehicle activity data, and the
option of modifying that data, so it can
be used to estimate a motor vehicle
emissions inventory in tons/day for a
specific year, month, or season, and as
a function of ambient temperature,
relative humidity, vehicle population,
mileage accrual, miles of travel and
speeds. Thus the model can be used to
make decisions about air pollution
policies and programs at the local or
state level. Inventories based on EMFAC
are also used to meet the federal CAA’s
SIP and transportation conformity
requirements. Transportation
conformity is required under CAA
section 176(c) to ensure that federally
supported transportation plans,
transportation improvement programs
(TIPs), and highway and transit projects
are consistent with (‘‘conform to’’) the
purpose of the SIP. Conformity to a SIP
means that a transportation activity will
not cause or contribute to new air
quality violations, worsen existing
violations, or delay timely attainment of
the national ambient air quality
standards (NAAQS) or interim
milestones. EPA’s transportation
conformity regulations (40 CFR Parts
51.390 and 93) describe how federally
funded and approved highway and
transit projects meet these statutory
requirements.
B. What versions of EMFAC are
currently in use in California?
Most SIPs in California were
developed using EMFAC2007 (released
by CARB in October 2007) or
EMFAC2002 (released by CARB in
October 2002). EPA approved
EMFAC2007 on January 18, 2008 (73 FR
3464) and approved EMFAC2002 on
April 1, 2003 (68 FR 15720) for all areas
in California.
EMFAC2007 was considered a major
update to previous versions of EMFAC
and most SIPs in California were
updated with EMFAC2007 in the 2007–
2008 timeframe. EMFAC2007 included
new data and methodologies regarding
calculation of motor vehicle emissions,
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14533
and revisions to implementation data
for control measures.
C. Why is EPA announcing its approval
of the EMFAC model?
CAA section 172(c)(3) and 40 CFR
51.112(a)(1) require that SIP inventories
be based on the most current, accurate,
and applicable models that are available
at the time the SIP is developed. CAA
section 176(c)(1) requires that the latest
emissions estimates be used in
conformity analyses. EPA approves
models that fulfill these requirements.
Under 40 CFR 93.111(a), EPA must
approve new versions of EMFAC for SIP
purposes before they can be used in
transportation conformity analyses. In
an April 6, 2012 letter, CARB requested
that EPA approve EMFAC2011 for use
in developing SIPs and in determining
conformity in California.1 EMFAC2011
is a significant change from previous
EMFAC models with a new model user
interface and is capable of calculating
motor vehicle emissions for all
California areas. EMFAC2011 is being
approved as the latest emissions model
for statewide use in SIP development
and emissions analyses for conformity
purposes. Since the EMFAC model is
only used in California, EPA’s statewide
approval of the model does not affect
MOVES emissions factor model users in
other states.
II. EPA Action
A. What version of EMFAC is EPA
approving?
In this notice, EPA is approving and
announcing that EMFAC2011 is
available to use in statewide California
SIP development and for regional
emissions analyses and CO, PM10 and
PM2.5 hot-spot analyses for
transportation conformity. EMFAC2011
was developed by CARB and
transmitted for approval to EPA on
April 6, 2012.
The EMFAC2011 model is composed
of a new modular structure that will
facilitate future model updates and
allow CARB to incorporate updated
information about truck and bus activity
and emissions data into the model. The
three major modules of EMFAC include
EMFAC–LDV, EMFAC–HD and
EMFAC–SG. EMFAC–LDV can be used
to estimate emissions for gasoline
powered on-road vehicles and smaller
on-road diesel vehicles and urban
transit buses. EMFAC–HD provides
1 The EMFAC2011 model and supporting
information is available for downloading at https://
www.arb.ca.gov/msei/modeling.htm. Technical
documentation explaining the changes to the model
and the technical foundations for the model is
available at https://www.arb.ca.gov/msei/emfac2011documentation-final.pdf.
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Federal Register / Vol. 78, No. 44 / Wednesday, March 6, 2013 / Notices
emissions factors for heavy-duty diesel
trucks and buses. EMFAC–SG allows
users to run one tool for SIP inventories
and regional emissions analyses to
combine the emissions factors from both
EMFAC–LDV and EMFAC–HD with
user defined vehicle miles of travel and
speeds, combine emissions from
multiple model-defined subareas and
incorporate reductions associated with
CARB’s Pavley and Low Carbon Fuel
standard regulations.
CARB developed the EMFAC–SG
module to provide users, including
transportation planners, with a
simplified method to generate emissions
with different future growth scenarios
for specific geographic areas needed for
transportation conformity and SIP
development. CARB also developed the
EMFAC–PL tool for use for doing
multiple model runs to extract
emissions factors for project-level
analyses needed for hot-spot analyses.2
Due to the modular structure of the
EMFAC2011 model, to obtain emissions
factors for project-level analyses, an
EMFAC2011 user would have to run
multiple modules to generate emission
factors. Therefore ARB has developed
the EMFAC–PL tool to produce
emissions factors for projects that are
consistent with the default assumptions
in EMFAC2011. For projects that have
site-specific ambient temperature and
relative humidity profiles, projectspecific vehicle age distributions and/or
project-specific rest and soak time data,
the user will have to use a more detailed
approach other than EMFAC–PL that
requires getting emissions factors from
EMFAC–LDV and EMFAC–HD. As
discussed later in this notice, EPA is
consulting with CARB to provide
updated EMFAC guidance for how to
apply the EMFAC2011 emissions model
through either the EMFAC–PL tool or
the more detailed approach that would
not use EMFAC–PL.
B. What analyses can EMFAC2011 be
used for?
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EPA is approving the model to
estimate regional emissions of HC, CO,
NOX, PM10, PM2.5, lead, and sulfur
oxides.3 However, EMFAC2011 will
only be used in transportation
conformity for pollutants and precursors
that affect transportation-related
2 The EMFAC–PL tool is available at: https://
www.arb.ca.gov/msei/modeling.htm. In an email to
EPA dated 2/08/2013, CARB clarified that the
EMFAC–PL tool is available for use in project-level
assessments.
3 EPA notes that EMFAC2011 can be used for CO
2
emissions analyses as well, but there are no SIP or
transportation conformity requirements for
greenhouse gases (GHGs).
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emissions, e.g., HC, NOX, CO, PM10 and
PM2.5.
EPA is also approving EMFAC2011 to
estimate CO, PM10 and PM2.5 emissions
for conformity hot-spot analyses
involving individual transportation
projects. A hot-spot analysis is defined
in 40 CFR 93.101 as an estimation of
likely future localized pollutant
concentrations and a comparison of
those concentrations to the relevant
NAAQS. This analysis is conducted on
a smaller scale than a nonattainment or
maintenance area, e.g., for a congested
roadway intersection.
EPA also notes that today’s approval
action does not impact what
methodology is required for calculating
re-entrained road dust for regional PM10
and PM2.5 SIPs and transportation
conformity analyses. EMFAC2011’s
PM10 and PM2.5 estimates do not include
such emissions. When applicable, PM10
and PM2.5 nonattainment and
maintenance areas are required to use
EPA’s AP–42 road dust method for
calculating road dust emissions, unless
a local method is approved in advance
by EPA.4 In addition, EMFAC2011 does
not estimate ammonia emissions; air
quality and transportation agencies
should contact the EPA Regional Office
if ammonia emissions estimates are
needed for SIPs or regional conformity
emissions analyses.
C. Why is EMFAC2011 being approved
for PM10 and PM2.5 hot-spot analyses at
this time?
conformity purposes within California.
As mentioned earlier, CARB has
developed the EMFAC–PL tool, as a
simplified method to extract the
appropriate emissions factors for
alternative vehicle data and speeds from
EMFAC2011 for appropriate projects. In
today’s notice, EPA recognizes the
importance of this tool for ensuring that
project-level conformity analyses are
done in a consistent and accurate
matter. To that end, we are also
approving the EMFAC–PL tool for
project-level conformity analyses, and
allowing other tools to be approved by
EPA, if such alternate project-level tools
provide for similar performance in
applying EMFAC2011 emissions factors
for appropriate projects.5 EPA is
updating Section 5 and related
appendices of our PM hot-spot
quantitative guidance to describe how to
use the EMFAC2011 model for PM hotspot analyses.6 EPA’s revised guidance
will include details on what PM hotspot analyses can rely on the EMFAC–
PL tool and which projects will require
a different approach to obtain the
appropriate project-level EMFAC2011
emission factors. EPA intends to
complete its PM hot-spot guidance
revision in the near future. When
completed, the updated guidance will
be made available on EPA’s Web site:
www.epa.gov/otaq/stateresources/
transconf/projectlevel-hotspot.htm.
On December 20, 2010, EPA
published a notice which announced
the availability of EPA guidance
documents for completing quantitative
hot-spot analyses and approved the use
of the MOVES and the EMFAC2007
models for use in quantitative PM10 and
PM2.5 hot-spot analyses (75 FR 79370).
That notice started a two-year grace
period requiring project sponsors to use
EMFAC2007 for new quantitative PM10
and PM2.5 hot-spot analyses in
California, for conformity
determinations involving projects of
local air quality concern.
As with EMFAC2007, EMFAC2011 is
capable of assessing project-level
emissions for PM10 and PM2.5 hot-spot
analyses, therefore EPA is approving
EMFAC2011 for use in quantitative PM
hot-spot analyses for transportation
D. Why does EPA consider EMFAC2011
as a major update to EMFAC?
EMFAC2011 includes significant
changes to its model interface, new data
and methodologies regarding
calculation of motor vehicle emissions
and revisions to implementation data
for control measures. EMFAC2011
includes updated data on truck activity,
and emissions reductions associated
with the 2010 Truck and Bus rule,
supporting new estimates of emissions
from heavy-heavy duty diesel trucks
and buses. Motor vehicle fleet age,
vehicle types and vehicle population
have also been updated based on 2009
California Department of Motor Vehicle
(DMV) data. EMFAC2011 incorporates
new temperature and humidity profiles.
Each of these changes impact emission
factors for each area in California. In
addition to changes to truck activity,
EMFAC incorporates updated vehicle
4 For further information, see EPA’s February 4,
2011 Notice of Availability for the January 2011
AP–42 Method for Estimating Re-entrained Road
Dust from Paved Roads (76 FR 6328). Also, for
using AP–42 for unpaved roads, see EPA’s August
2, 2007 memorandum, ‘‘Policy Guidance on the Use
of the November 1, 2006, Update to AP–42 for Reentrained Road Dust for SIP Development and
Transportation Conformity.’’
5 EPA would approve any alternate project-level
tool through a letter, after completion of its review
of model documentation showing consistency with
the EMFAC–PL approach.
6 ‘‘Transportation Conformity Guidance for
Quantitative Hot-Spot Analyses in PM2.5 and PM10
Nonattainment and Maintenance Areas’’ [EPA–420–
B–10–040]. See www.epa.gov/otaq/stateresources/
transconf/projectlevel-hotspot.htm.
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F. Will a transportation conformity
grace period be set by this approval?
Yes. The transportation conformity
rule (40 CFR 93.111) requires that
conformity analyses be based on the
latest motor vehicle emissions model
approved by EPA for SIP purposes for
a state or area. Section 176(c)(1) of the
CAA states that
E. How were stakeholders and the
public involved in the EMFAC
development process?
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miles traveled (VMT) for all vehicle
classes. The new model interface
EMFAC–SG module will allow users to
update the default VMT data and speed
profiles by vehicle class for different
future scenarios. CARB’s web site
describes these and other model
changes at: https://www.arb.ca.gov/msei/
emfac2011-documentation-final.pdf.
‘‘ * * * [t]he determination of conformity
shall be based on the most recent estimates
of emissions, and such estimates shall be
determined from the most recent population,
employment, travel, and congestion
estimates. * * *’’
Since 2010, CARB has held a series of
public workshops to discuss emissions
inventory updates related to California’s
In-Use Heavy-Duty Diesel Fueled Truck
and Bus regulation (‘‘Truck and Bus
Regulation’’), and to receive comments
on the regulations and the resulting
changes in the emissions inventory.
Since the major changes to the EMFAC
model are associated with incorporation
of the Truck and Bus Regulation into the
model, the technical foundations of
these changes were presented to the
public in these workshops. CARB also
conducted extensive beta testing of
interim versions of the model with air
districts and Metropolitan Planning
Organizations (MPOs). These
stakeholders had the opportunity to
request briefings with CARB staff and
provide them with comments and
suggestions to improve the model. EPA
was included in those discussions and
our suggestions were incorporated into
the material available on the CARB
EMFAC2011 public web site. CARB also
developed and posted training modules
for EMFAC2011 and supports a mobile
source emissions inventory email
listserv to announce updates and
changes to the EMFAC supporting
material.7
CARB also released a series of
technical memos that describe each
update to the model and public
presentations that summarize the
changes from earlier versions of the
model. The technical memos are
available on CARB’s Web site at: https://
www.arb.ca.gov/msei/supportdocs.htm
and at https://www.arb.ca.gov/msei/
categories.htm#onroad_motor_vehicles
Specific changes incorporated into the
EMFAC2011 model are also discussed
in https://www.arb.ca.gov/msei/
emfac2011-documentation-final.pdf. All
presentations from the public
workshops are available on the CARB
Web site at: https://www.arb.ca.gov/
msprog/onrdiesel/workshops.htm.
7 To subscribe to CARB’s listserv for Mobile
Source Emission Inventory development, see ‘‘Join
our MSEI listserv’’ at www.arb.ca.gov/msei/
msei.htm.
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When EPA approves a new emissions
model such as EMFAC2011, EPA will
consult with the U.S. Department of
Transportation (DOT) to establish a
grace period before the model is
required for conformity analyses (40
CFR 93.111(b)). However, areas have the
option of using the new model prior to
the end of the grace period. The
conformity rule provides for a grace
period for new emissions models of
between 3 to 24 months. In consultation
with the Federal Highway
Administration (FHWA) and the Federal
Transit Administration (FTA), EPA
considers many factors in establishing
the length of the grace period, including
the degree of change in emissions
models and the effects of the new model
on transportation planning in order to
assure conformity (40 CFR 93.111).
Upon consideration of all of these
factors, EPA is establishing a 6-month
grace period before EMFAC2011 is
required for the following conformity
analyses:
• All new HC, NOX, PM10, PM2.5 and
CO regional emissions analyses (e.g.,
supporting transportation plan and TIP
conformity determinations); and
• All new CO, PM10 and PM2.5 hotspot analyses supporting project-level
conformity determinations.
The grace period begins on March 6,
2013 and ends on September 6, 2013. As
discussed earlier in the notice,
EMFAC2011 incorporates significant
changes to the model interface and
procedures used to estimate both
emissions for regional emissions
analysis and emissions factors for hotspot analyses for CO and PM. While
these changes are significant, the model
has been available for review by air
quality and transportation agencies,
consultants and the public since
September 2011.
For application of EMFAC2011 at the
project level, CARB’s EMFAC–PL tool
for appropriate projects has just recently
been released, therefore project sponsors
developing project-level analysis may
need some time to familiarize
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14535
themselves with this tool. EPA is also
updating our PM hot-spot quantitative
guidance to include the new
EMFAC2011 procedures.
Therefore, it is appropriate to set a 6month grace period to allow all areas in
California to incorporate these new
procedures in conformity hot-spot
analysis 8 and apply the changes to the
model structure and updated planning
assumptions incorporated in
EMFAC2011 in a timely manner. In the
interim, new quantitative PM hot-spot
analyses that are started prior to the end
of the EMFAC2011 grace period can be
based on EMFAC2007 and EPA’s
existing PM hot-spot guidance and
subsequently completed.
When the grace period ends on
September 6, 2013, EMFAC2011 will
become the only approved motor
vehicle emissions model for all new
regional and CO, PM10 and PM2.5 hotspot transportation conformity analyses
across California. In general, this means
that all new HC, NOX, PM10, PM2.5, and
CO regional conformity analyses and
CO, PM10 and PM2.5 hot-spot analyses
started after the end of the 6-month
grace period must be based on
EMFAC2011, even if the SIP is based on
an earlier version of the EMFAC model.
G. Can areas use any other models
during the grace period?
Yes, the conformity rule provides
some flexibility for regional emissions
analyses that are started before the end
of the grace period. Analyses that begin
before or during the grace period may
continue to rely on EMFAC2007. The
interagency consultation process should
be used if it is unclear if an
EMFAC2007-based analysis was begun
before the end of the grace period. When
the grace period ends on September 6,
2013, EMFAC2011 will become the only
approved motor vehicle emissions
model for regional emissions analyses
for transportation conformity in
California.
CO, PM10 and PM2.5 hot-spot analyses
for project-level conformity
determinations can be based on
EMFAC2007 if the analysis was begun
before the end of the grace period, and
if the final environmental document for
the project is issued no more than three
years after the issuance of the draft
environmental document (see 40 CFR
93.111(c)). Therefore new quantitative
and qualitative analysis already
underway that were started before the
8 EMFAC–PL or an alternative method or tool
must be used for new EMFAC2011 analyses of
appropriate projects after the 6-month grace period.
If EPA approves alternative tools to the EMFAC–PL
tool, EPA does not intend to establish a new 6month grace period.
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Federal Register / Vol. 78, No. 44 / Wednesday, March 6, 2013 / Notices
end of the grace period using
EMFAC2007 can be completed as long
as 93.111(c) is satisfied. The interagency
consultation process should be used if
it is unclear whether an EMFAC2007based analysis is covered by the
circumstances described above.
Dated: February 22, 2013.
Jared Blumenfeld,
Regional Administrator, Region IX.
H. Future Updates to EMFAC
ENVIRONMENTAL PROTECTION
AGENCY
On January 31, 2006, CARB submitted
a letter to EPA and to the California
Division of the FHWA indicating the
State’s intention to make future
revisions to update EMFAC. These
EMFAC updates would reflect, among
other new information, updated vehicle
fleet data every three years. In
California, MPOs and Air Districts have
not been able to update vehicle fleet
data embedded into EMFAC. The EPA/
USDOT December 2008 guidance on
latest planning assumptions and EPA’s
July 2004 final rule indicate that new
vehicle registration data must be used
when it is available prior to the start of
new conformity analyses and that states
and MPOs are strongly encouraged to
update the data at least every five years.
CARB reaffirmed their commitment to
keeping the latest planning assumptions
included in EMFAC updated on a threeyear cycle in the April 18, 2007 EMFAC
submittal letter. The next update to the
planning assumptions in EMFAC is
expected in 2014 or 2015 which would
most likely also include updates to the
emissions factors of the model as well.
[FRL–9787–2 ]
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III. Summary of EPA Actions
As described in this notice, EPA is
approving EMFAC2011 as submitted by
CARB on April 6, 2012 with the
following limitations and conditions:
(1) The approval is limited to
California.
(2) The approval is Statewide and
applies to estimation of emissions of
HC, CO, NOX, PM10, PM2.5, lead, and
sulfur oxides. However, EMFAC2011
will be used in transportation
conformity regional emissions analyses
for pollutants and precursors that are
applicable in a given nonattainment or
maintenance area. EPA is approving all
components of EMFAC2011,
specifically EMFAC–SG, EMFAC–LDV
and EMFAC–HD. EPA is also approving
EMFAC2011 and the EMFAC–PL tool to
estimate project-level emissions for CO,
PM10 and PM2.5 conformity hot-spot
analyses.
(3) A 6-month statewide
transportation conformity grace period
will be established beginning March 6,
2013 and ending September 6, 2013 for
the transportation conformity uses
described in (2) above.
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[FR Doc. 2013–05245 Filed 3–5–13; 8:45 am]
BILLING CODE 6560–50–P
Notification of a Public Teleconference
of the Chartered Science Advisory
Board
Environmental Protection
Agency (EPA).
ACTION: Notice.
AGENCY:
SUMMARY: The EPA Science Advisory
Board (SAB) Staff Office announces a
public teleconference of the chartered
SAB to conduct a quality review of an
SAB draft report on approaches to
derive a maximum contaminant level
goal for perchlorate.
DATES: The public teleconference will
be held on March 29, 2013, from 1:00
p.m. to 4:00 p.m.
ADDRESSES: The public teleconference
will be conducted by telephone only.
FOR FURTHER INFORMATION CONTACT: Any
member of the public wishing to obtain
general information regarding the
quality review teleconference should
contact Dr. Angela Nugent, Designated
Federal Officer (DFO), EPA Science
Advisory Board (1400R), 1200
Pennsylvania Avenue NW., Washington,
DC 20460; via telephone/voice mail
(202) 564–2218; fax (202) 565–2098 or
via email at nugent.angela@epa.gov.
General information concerning the EPA
Science Advisory Board can be found
on the SAB Web site at https://
www.epa.gov/sab.
SUPPLEMENTARY INFORMATION: Pursuant
to the Federal Advisory Committee Act
(FACA), 5 U.S.C., App. 2, notice is
hereby given that the EPA Science
Advisory Board will hold a public
teleconference to conduct a quality
review of an SAB draft report. The SAB
was established pursuant to 42 U.S.C.
4365 to provide independent scientific
and technical advice to the
Administrator on the technical basis for
Agency positions and regulations. The
SAB is a Federal Advisory Committee
under FACA. The SAB will comply
with the provisions of FACA and all
appropriate SAB Staff Office procedural
policies.
Background
Quality review is a key function of the
chartered SAB. Draft reports prepared
by SAB committees, panels, or work
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groups must be reviewed and approved
by the chartered SAB before transmittal
to the EPA Administrator. The chartered
SAB makes a determination in a public
meeting consistent with FACA about the
quality of all draft reports and
determines whether the report is ready
to be transmitted to the EPA
Administrator.
The Safe Drinking Water Act requires
the EPA to request comments from the
SAB prior to proposal of a maximum
contaminant level goal (MCLG) and
national primary drinking water
regulation. The chartered SAB will
conduct a quality review of a draft SAB
report reviewing the scientific and
technical bases for the approaches EPA
is considering for the MCLG for
perchlorate, as described in a draft
white paper entitled ‘‘Life Stage
Considerations and Interpretation of
Recent Epidemiological Evidence to
Develop a Maximum Contaminant Level
Goal for Perchlorate.’’ Background
information about this advisory activity
can be found on the SAB Web site at
https://yosemite.epa.gov/sab/sab
product.nsf/fedrgstr_activites/
Perchlorate%20MCLG%20Approaches
?OpenDocument.
Availability of Meeting Materials: The
agenda and other materials in support of
the teleconference will be placed on the
SAB Web site at https://www.epa.gov/sab
in advance of the teleconference.
Procedures for Providing Public Input:
Public comment for consideration by
EPA’s federal advisory committees and
panels has a different purpose from
public comment provided to EPA
program offices. Therefore, the process
for submitting comments to a federal
advisory committee is different from the
process used to submit comments to an
EPA program office. Federal advisory
committees and panels, including
scientific advisory committees, provide
independent advice to EPA. Members of
the public can submit relevant
comments pertaining to the group
providing advice, EPA’s charge
questions and EPA review or
background documents. Input from the
public to the SAB will have the most
impact if it consists of comments that
provide specific scientific or technical
information or analysis for the SAB to
consider or if it relates to the clarity or
accuracy of the technical information.
Members of the public wishing to
provide comment should contact the
DFO for the relevant advisory
committee directly. Oral Statements: In
general, individuals or groups
requesting time to make an oral
presentation at a public SAB
teleconference will be limited to three
minutes. Those interested in being
E:\FR\FM\06MRN1.SGM
06MRN1
Agencies
[Federal Register Volume 78, Number 44 (Wednesday, March 6, 2013)]
[Notices]
[Pages 14533-14536]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2013-05245]
[[Page 14533]]
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ENVIRONMENTAL PROTECTION AGENCY
[EPA-R09-OAR-2013-0126; FRL-9788-3]
Official Release of EMFAC2011 Motor Vehicle Emission Factor Model
for Use in the State of California
AGENCY: Environmental Protection Agency (EPA).
ACTION: Notice of Availability.
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SUMMARY: EPA is approving and announcing the availability of the latest
version of the California EMFAC model (short for EMission FACtor) for
use in state implementation plan (SIP) development and transportation
conformity in California. EMFAC2011 is the latest update to the EMFAC
model for use by California state and local governments to meet Clean
Air Act (CAA) requirements. The new model, which is based on new and
improved data, calculates air pollution emissions factors for passenger
cars, trucks, motorcycles, motor homes and buses. Today's notice also
sets the date after which EMFAC2011 is required to be used statewide in
all new regional emissions analyses and carbon monoxide (CO),
particulate matter of ten microns or less (PM10) and fine
particulate matter (PM2.5) hot-spot analyses for
transportation conformity determinations in California. Since the EMFAC
model is used only in California, EPA's approval of the model does not
affect MOVES model users in other states.
DATES: EPA's approval of the EMFAC2011 emissions model for SIP and
conformity purposes is effective March 6, 2013. EMFAC2011 must be used
for all new regional emissions analyses and CO, PM10 and
PM2.5 hot-spot analyses that are started on or after
September 6, 2013.
FOR FURTHER INFORMATION CONTACT: Karina O'Connor,
oconnor.karina@epa.gov, (775) 433-8176, Air Planning Office (AIR-2),
Air Division, U.S. EPA, Region 9, 75 Hawthorne Street, San Francisco,
California, 94105-3901.
SUPPLEMENTARY INFORMATION: Copies of the official version of the
EMFAC2011 model are available on the California Air Resources Board
(CARB) Web site: https://www.arb.ca.gov/msei/modeling.htm (model,
technical support documents, etc.).
I. Background
A. What is the EMFAC model?
The EMFAC model is a computer model that can estimate emission
rates for on-road mobile sources (``motor vehicles'') for calendar
years from 1990 to 2035 operating in California. Pollutant emissions
for hydrocarbons (HC), CO, nitrogen oxides (NOX),
PM10, PM2.5, lead, carbon dioxide
(CO2), and sulfur oxides are output from the model.
Emissions are calculated for forty-two different vehicle classes
composed of passenger cars, various types of trucks and buses,
motorcycles, and motor homes.
EMFAC is used to calculate current and future inventories of motor
vehicle emissions at the state, air district, air basin, or county
level. EMFAC contains default vehicle activity data, and the option of
modifying that data, so it can be used to estimate a motor vehicle
emissions inventory in tons/day for a specific year, month, or season,
and as a function of ambient temperature, relative humidity, vehicle
population, mileage accrual, miles of travel and speeds. Thus the model
can be used to make decisions about air pollution policies and programs
at the local or state level. Inventories based on EMFAC are also used
to meet the federal CAA's SIP and transportation conformity
requirements. Transportation conformity is required under CAA section
176(c) to ensure that federally supported transportation plans,
transportation improvement programs (TIPs), and highway and transit
projects are consistent with (``conform to'') the purpose of the SIP.
Conformity to a SIP means that a transportation activity will not cause
or contribute to new air quality violations, worsen existing
violations, or delay timely attainment of the national ambient air
quality standards (NAAQS) or interim milestones. EPA's transportation
conformity regulations (40 CFR Parts 51.390 and 93) describe how
federally funded and approved highway and transit projects meet these
statutory requirements.
B. What versions of EMFAC are currently in use in California?
Most SIPs in California were developed using EMFAC2007 (released by
CARB in October 2007) or EMFAC2002 (released by CARB in October 2002).
EPA approved EMFAC2007 on January 18, 2008 (73 FR 3464) and approved
EMFAC2002 on April 1, 2003 (68 FR 15720) for all areas in California.
EMFAC2007 was considered a major update to previous versions of
EMFAC and most SIPs in California were updated with EMFAC2007 in the
2007-2008 timeframe. EMFAC2007 included new data and methodologies
regarding calculation of motor vehicle emissions, and revisions to
implementation data for control measures.
C. Why is EPA announcing its approval of the EMFAC model?
CAA section 172(c)(3) and 40 CFR 51.112(a)(1) require that SIP
inventories be based on the most current, accurate, and applicable
models that are available at the time the SIP is developed. CAA section
176(c)(1) requires that the latest emissions estimates be used in
conformity analyses. EPA approves models that fulfill these
requirements.
Under 40 CFR 93.111(a), EPA must approve new versions of EMFAC for
SIP purposes before they can be used in transportation conformity
analyses. In an April 6, 2012 letter, CARB requested that EPA approve
EMFAC2011 for use in developing SIPs and in determining conformity in
California.\1\ EMFAC2011 is a significant change from previous EMFAC
models with a new model user interface and is capable of calculating
motor vehicle emissions for all California areas. EMFAC2011 is being
approved as the latest emissions model for statewide use in SIP
development and emissions analyses for conformity purposes. Since the
EMFAC model is only used in California, EPA's statewide approval of the
model does not affect MOVES emissions factor model users in other
states.
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\1\ The EMFAC2011 model and supporting information is available
for downloading at https://www.arb.ca.gov/msei/modeling.htm.
Technical documentation explaining the changes to the model and the
technical foundations for the model is available at https://www.arb.ca.gov/msei/emfac2011-documentation-final.pdf.
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II. EPA Action
A. What version of EMFAC is EPA approving?
In this notice, EPA is approving and announcing that EMFAC2011 is
available to use in statewide California SIP development and for
regional emissions analyses and CO, PM10 and
PM2.5 hot-spot analyses for transportation conformity.
EMFAC2011 was developed by CARB and transmitted for approval to EPA on
April 6, 2012.
The EMFAC2011 model is composed of a new modular structure that
will facilitate future model updates and allow CARB to incorporate
updated information about truck and bus activity and emissions data
into the model. The three major modules of EMFAC include EMFAC-LDV,
EMFAC-HD and EMFAC-SG. EMFAC-LDV can be used to estimate emissions for
gasoline powered on-road vehicles and smaller on-road diesel vehicles
and urban transit buses. EMFAC-HD provides
[[Page 14534]]
emissions factors for heavy-duty diesel trucks and buses. EMFAC-SG
allows users to run one tool for SIP inventories and regional emissions
analyses to combine the emissions factors from both EMFAC-LDV and
EMFAC-HD with user defined vehicle miles of travel and speeds, combine
emissions from multiple model-defined subareas and incorporate
reductions associated with CARB's Pavley and Low Carbon Fuel standard
regulations.
CARB developed the EMFAC-SG module to provide users, including
transportation planners, with a simplified method to generate emissions
with different future growth scenarios for specific geographic areas
needed for transportation conformity and SIP development. CARB also
developed the EMFAC-PL tool for use for doing multiple model runs to
extract emissions factors for project-level analyses needed for hot-
spot analyses.\2\ Due to the modular structure of the EMFAC2011 model,
to obtain emissions factors for project-level analyses, an EMFAC2011
user would have to run multiple modules to generate emission factors.
Therefore ARB has developed the EMFAC-PL tool to produce emissions
factors for projects that are consistent with the default assumptions
in EMFAC2011. For projects that have site-specific ambient temperature
and relative humidity profiles, project-specific vehicle age
distributions and/or project-specific rest and soak time data, the user
will have to use a more detailed approach other than EMFAC-PL that
requires getting emissions factors from EMFAC-LDV and EMFAC-HD. As
discussed later in this notice, EPA is consulting with CARB to provide
updated EMFAC guidance for how to apply the EMFAC2011 emissions model
through either the EMFAC-PL tool or the more detailed approach that
would not use EMFAC-PL.
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\2\ The EMFAC-PL tool is available at: https://www.arb.ca.gov/msei/modeling.htm. In an email to EPA dated 2/08/2013, CARB
clarified that the EMFAC-PL tool is available for use in project-
level assessments.
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B. What analyses can EMFAC2011 be used for?
EPA is approving the model to estimate regional emissions of HC,
CO, NOX, PM10, PM2.5, lead, and sulfur
oxides.\3\ However, EMFAC2011 will only be used in transportation
conformity for pollutants and precursors that affect transportation-
related emissions, e.g., HC, NOX, CO, PM10 and
PM2.5.
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\3\ EPA notes that EMFAC2011 can be used for CO2
emissions analyses as well, but there are no SIP or transportation
conformity requirements for greenhouse gases (GHGs).
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EPA is also approving EMFAC2011 to estimate CO, PM10 and
PM2.5 emissions for conformity hot-spot analyses involving
individual transportation projects. A hot-spot analysis is defined in
40 CFR 93.101 as an estimation of likely future localized pollutant
concentrations and a comparison of those concentrations to the relevant
NAAQS. This analysis is conducted on a smaller scale than a
nonattainment or maintenance area, e.g., for a congested roadway
intersection.
EPA also notes that today's approval action does not impact what
methodology is required for calculating re-entrained road dust for
regional PM10 and PM2.5 SIPs and transportation
conformity analyses. EMFAC2011's PM10 and PM2.5
estimates do not include such emissions. When applicable,
PM10 and PM2.5 nonattainment and maintenance
areas are required to use EPA's AP-42 road dust method for calculating
road dust emissions, unless a local method is approved in advance by
EPA.\4\ In addition, EMFAC2011 does not estimate ammonia emissions; air
quality and transportation agencies should contact the EPA Regional
Office if ammonia emissions estimates are needed for SIPs or regional
conformity emissions analyses.
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\4\ For further information, see EPA's February 4, 2011 Notice
of Availability for the January 2011 AP-42 Method for Estimating Re-
entrained Road Dust from Paved Roads (76 FR 6328). Also, for using
AP-42 for unpaved roads, see EPA's August 2, 2007 memorandum,
``Policy Guidance on the Use of the November 1, 2006, Update to AP-
42 for Re-entrained Road Dust for SIP Development and Transportation
Conformity.''
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C. Why is EMFAC2011 being approved for PM10 and PM2.5 hot-spot analyses
at this time?
On December 20, 2010, EPA published a notice which announced the
availability of EPA guidance documents for completing quantitative hot-
spot analyses and approved the use of the MOVES and the EMFAC2007
models for use in quantitative PM10 and PM2.5
hot-spot analyses (75 FR 79370). That notice started a two-year grace
period requiring project sponsors to use EMFAC2007 for new quantitative
PM10 and PM2.5 hot-spot analyses in California,
for conformity determinations involving projects of local air quality
concern.
As with EMFAC2007, EMFAC2011 is capable of assessing project-level
emissions for PM10 and PM2.5 hot-spot analyses,
therefore EPA is approving EMFAC2011 for use in quantitative PM hot-
spot analyses for transportation conformity purposes within California.
As mentioned earlier, CARB has developed the EMFAC-PL tool, as a
simplified method to extract the appropriate emissions factors for
alternative vehicle data and speeds from EMFAC2011 for appropriate
projects. In today's notice, EPA recognizes the importance of this tool
for ensuring that project-level conformity analyses are done in a
consistent and accurate matter. To that end, we are also approving the
EMFAC-PL tool for project-level conformity analyses, and allowing other
tools to be approved by EPA, if such alternate project-level tools
provide for similar performance in applying EMFAC2011 emissions factors
for appropriate projects.\5\ EPA is updating Section 5 and related
appendices of our PM hot-spot quantitative guidance to describe how to
use the EMFAC2011 model for PM hot-spot analyses.\6\ EPA's revised
guidance will include details on what PM hot-spot analyses can rely on
the EMFAC-PL tool and which projects will require a different approach
to obtain the appropriate project-level EMFAC2011 emission factors. EPA
intends to complete its PM hot-spot guidance revision in the near
future. When completed, the updated guidance will be made available on
EPA's Web site: www.epa.gov/otaq/stateresources/transconf/projectlevel-hotspot.htm.
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\5\ EPA would approve any alternate project-level tool through a
letter, after completion of its review of model documentation
showing consistency with the EMFAC-PL approach.
\6\ ``Transportation Conformity Guidance for Quantitative Hot-
Spot Analyses in PM2.5 and PM10 Nonattainment
and Maintenance Areas'' [EPA-420-B-10-040]. See www.epa.gov/otaq/stateresources/transconf/projectlevel-hotspot.htm.
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D. Why does EPA consider EMFAC2011 as a major update to EMFAC?
EMFAC2011 includes significant changes to its model interface, new
data and methodologies regarding calculation of motor vehicle emissions
and revisions to implementation data for control measures. EMFAC2011
includes updated data on truck activity, and emissions reductions
associated with the 2010 Truck and Bus rule, supporting new estimates
of emissions from heavy-heavy duty diesel trucks and buses. Motor
vehicle fleet age, vehicle types and vehicle population have also been
updated based on 2009 California Department of Motor Vehicle (DMV)
data. EMFAC2011 incorporates new temperature and humidity profiles.
Each of these changes impact emission factors for each area in
California. In addition to changes to truck activity, EMFAC
incorporates updated vehicle
[[Page 14535]]
miles traveled (VMT) for all vehicle classes. The new model interface
EMFAC-SG module will allow users to update the default VMT data and
speed profiles by vehicle class for different future scenarios. CARB's
web site describes these and other model changes at: https://www.arb.ca.gov/msei/emfac2011-documentation-final.pdf.
E. How were stakeholders and the public involved in the EMFAC
development process?
Since 2010, CARB has held a series of public workshops to discuss
emissions inventory updates related to California's In-Use Heavy-Duty
Diesel Fueled Truck and Bus regulation (``Truck and Bus Regulation''),
and to receive comments on the regulations and the resulting changes in
the emissions inventory. Since the major changes to the EMFAC model are
associated with incorporation of the Truck and Bus Regulation into the
model, the technical foundations of these changes were presented to the
public in these workshops. CARB also conducted extensive beta testing
of interim versions of the model with air districts and Metropolitan
Planning Organizations (MPOs). These stakeholders had the opportunity
to request briefings with CARB staff and provide them with comments and
suggestions to improve the model. EPA was included in those discussions
and our suggestions were incorporated into the material available on
the CARB EMFAC2011 public web site. CARB also developed and posted
training modules for EMFAC2011 and supports a mobile source emissions
inventory email listserv to announce updates and changes to the EMFAC
supporting material.\7\
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\7\ To subscribe to CARB's listserv for Mobile Source Emission
Inventory development, see ``Join our MSEI listserv'' at
www.arb.ca.gov/msei/msei.htm.
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CARB also released a series of technical memos that describe each
update to the model and public presentations that summarize the changes
from earlier versions of the model. The technical memos are available
on CARB's Web site at: https://www.arb.ca.gov/msei/supportdocs.htm and
at https://www.arb.ca.gov/msei/categories.htm#onroad_motor_vehicles
Specific changes incorporated into the EMFAC2011 model are also
discussed in https://www.arb.ca.gov/msei/emfac2011-documentation-final.pdf. All presentations from the public workshops are available on
the CARB Web site at: https://www.arb.ca.gov/msprog/onrdiesel/workshops.htm.
F. Will a transportation conformity grace period be set by this
approval?
Yes. The transportation conformity rule (40 CFR 93.111) requires
that conformity analyses be based on the latest motor vehicle emissions
model approved by EPA for SIP purposes for a state or area. Section
176(c)(1) of the CAA states that
`` * * * [t]he determination of conformity shall be based on the
most recent estimates of emissions, and such estimates shall be
determined from the most recent population, employment, travel, and
congestion estimates. * * *''
When EPA approves a new emissions model such as EMFAC2011, EPA will
consult with the U.S. Department of Transportation (DOT) to establish a
grace period before the model is required for conformity analyses (40
CFR 93.111(b)). However, areas have the option of using the new model
prior to the end of the grace period. The conformity rule provides for
a grace period for new emissions models of between 3 to 24 months. In
consultation with the Federal Highway Administration (FHWA) and the
Federal Transit Administration (FTA), EPA considers many factors in
establishing the length of the grace period, including the degree of
change in emissions models and the effects of the new model on
transportation planning in order to assure conformity (40 CFR 93.111).
Upon consideration of all of these factors, EPA is establishing a
6-month grace period before EMFAC2011 is required for the following
conformity analyses:
All new HC, NOX, PM10,
PM2.5 and CO regional emissions analyses (e.g., supporting
transportation plan and TIP conformity determinations); and
All new CO, PM10 and PM2.5 hot-spot
analyses supporting project-level conformity determinations.
The grace period begins on March 6, 2013 and ends on September 6,
2013. As discussed earlier in the notice, EMFAC2011 incorporates
significant changes to the model interface and procedures used to
estimate both emissions for regional emissions analysis and emissions
factors for hot-spot analyses for CO and PM. While these changes are
significant, the model has been available for review by air quality and
transportation agencies, consultants and the public since September
2011.
For application of EMFAC2011 at the project level, CARB's EMFAC-PL
tool for appropriate projects has just recently been released,
therefore project sponsors developing project-level analysis may need
some time to familiarize themselves with this tool. EPA is also
updating our PM hot-spot quantitative guidance to include the new
EMFAC2011 procedures.
Therefore, it is appropriate to set a 6-month grace period to allow
all areas in California to incorporate these new procedures in
conformity hot-spot analysis \8\ and apply the changes to the model
structure and updated planning assumptions incorporated in EMFAC2011 in
a timely manner. In the interim, new quantitative PM hot-spot analyses
that are started prior to the end of the EMFAC2011 grace period can be
based on EMFAC2007 and EPA's existing PM hot-spot guidance and
subsequently completed.
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\8\ EMFAC-PL or an alternative method or tool must be used for
new EMFAC2011 analyses of appropriate projects after the 6-month
grace period. If EPA approves alternative tools to the EMFAC-PL
tool, EPA does not intend to establish a new 6-month grace period.
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When the grace period ends on September 6, 2013, EMFAC2011 will
become the only approved motor vehicle emissions model for all new
regional and CO, PM10 and PM2.5 hot-spot
transportation conformity analyses across California. In general, this
means that all new HC, NOX, PM10,
PM2.5, and CO regional conformity analyses and CO,
PM10 and PM2.5 hot-spot analyses started after
the end of the 6-month grace period must be based on EMFAC2011, even if
the SIP is based on an earlier version of the EMFAC model.
G. Can areas use any other models during the grace period?
Yes, the conformity rule provides some flexibility for regional
emissions analyses that are started before the end of the grace period.
Analyses that begin before or during the grace period may continue to
rely on EMFAC2007. The interagency consultation process should be used
if it is unclear if an EMFAC2007-based analysis was begun before the
end of the grace period. When the grace period ends on September 6,
2013, EMFAC2011 will become the only approved motor vehicle emissions
model for regional emissions analyses for transportation conformity in
California.
CO, PM10 and PM2.5 hot-spot analyses for
project-level conformity determinations can be based on EMFAC2007 if
the analysis was begun before the end of the grace period, and if the
final environmental document for the project is issued no more than
three years after the issuance of the draft environmental document (see
40 CFR 93.111(c)). Therefore new quantitative and qualitative analysis
already underway that were started before the
[[Page 14536]]
end of the grace period using EMFAC2007 can be completed as long as
93.111(c) is satisfied. The interagency consultation process should be
used if it is unclear whether an EMFAC2007-based analysis is covered by
the circumstances described above.
H. Future Updates to EMFAC
On January 31, 2006, CARB submitted a letter to EPA and to the
California Division of the FHWA indicating the State's intention to
make future revisions to update EMFAC. These EMFAC updates would
reflect, among other new information, updated vehicle fleet data every
three years. In California, MPOs and Air Districts have not been able
to update vehicle fleet data embedded into EMFAC. The EPA/USDOT
December 2008 guidance on latest planning assumptions and EPA's July
2004 final rule indicate that new vehicle registration data must be
used when it is available prior to the start of new conformity analyses
and that states and MPOs are strongly encouraged to update the data at
least every five years. CARB reaffirmed their commitment to keeping the
latest planning assumptions included in EMFAC updated on a three-year
cycle in the April 18, 2007 EMFAC submittal letter. The next update to
the planning assumptions in EMFAC is expected in 2014 or 2015 which
would most likely also include updates to the emissions factors of the
model as well.
III. Summary of EPA Actions
As described in this notice, EPA is approving EMFAC2011 as
submitted by CARB on April 6, 2012 with the following limitations and
conditions:
(1) The approval is limited to California.
(2) The approval is Statewide and applies to estimation of
emissions of HC, CO, NOX, PM10, PM2.5,
lead, and sulfur oxides. However, EMFAC2011 will be used in
transportation conformity regional emissions analyses for pollutants
and precursors that are applicable in a given nonattainment or
maintenance area. EPA is approving all components of EMFAC2011,
specifically EMFAC-SG, EMFAC-LDV and EMFAC-HD. EPA is also approving
EMFAC2011 and the EMFAC-PL tool to estimate project-level emissions for
CO, PM10 and PM2.5 conformity hot-spot analyses.
(3) A 6-month statewide transportation conformity grace period will
be established beginning March 6, 2013 and ending September 6, 2013 for
the transportation conformity uses described in (2) above.
Dated: February 22, 2013.
Jared Blumenfeld,
Regional Administrator, Region IX.
[FR Doc. 2013-05245 Filed 3-5-13; 8:45 am]
BILLING CODE 6560-50-P