Notice of Supplemental Determination for Renewable Fuels Produced Under the Final RFS2 Program From Canola Oil, 43522-43526 [2010-18227]
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of the 2005 National-Scale Air Toxics
Assessment/National Emissions
Inventory (NATA/NEI) data sets and
more specific information needed for
further rulemaking would be derived
from the ICR. Information collected
directly from companies owning or
operating secondary aluminum
production facilities will have the
greatest practical utility for purposes of
performing the RTR as information from
the affected industry will contain the
most up-to-date, accurate, and reliable
equipment and operational data for each
facility.
It is essential for the EPA to have an
updated database reflecting the postMACT configurations of secondary
aluminum manufacturing affected
sources and air pollution control
systems to use in the regulatory analyses
required under CAA sections 112(d) and
(f).
The data collected will be used to
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This information, along with existing
permitted emission limits will be used
to establish a baseline for purposes of
the regulatory reviews. The emissions
test data collected will be used to verify
the performance of existing control
measures, examine variability in
emissions, evaluate emission limits, and
to determine the performance of
superior control measures that may be
considered for purposes of reducing
residual risk. Emissions data may also
be used along with process and
emission unit details to consider
subcategories for further regulation and
to estimate the environmental and cost
impacts associated with any regulatory
options considered.
In addition to informing the RTR
regulatory analyses for the secondary
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EPA’s intent that the NATA/NEI
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versions of the NATA/NEI and its
successor, the Emissions Inventory
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and the public for a variety of purposes
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pollutants. More information in the NEI
can be found at https://www.epa.gov/air/
data/neidb.html.
This collection of information is
mandatory under CAA section 114 (42
U.S.C. 7414). All information submitted
to EPA pursuant to this ICR for which
a claim of confidentiality is made is
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safeguarded according to Agency
policies in 40 CFR part 2, subpart B.
Burden Statement: The projected cost
and hour burden for industry for this
one-time collection of information is
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burden is based on an estimated 400
respondents to the survey. This ICR
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either capital or start-up costs.
Operation and maintenance costs of
$1200 are estimated for postage to mail
in the survey response to EPA. Burden
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and transmit or otherwise disclose the
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The ICR provides a detailed
explanation of the Agency’s estimate,
which is only briefly summarized here.
Estimated total number of potential
respondents: 400.
Frequency of response: One time.
Estimated total average number of
responses for each respondent: 1.
Estimated total annual burden hours:
36,248.
Estimated total annual burden costs:
$3,430,000.
What is the next step in the process for
this ICR?
EPA will consider the comments
received and amend the ICR as
appropriate. The final ICR package will
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and approval pursuant to 5 CFR
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pursuant to 5 CFR 1320.5(a)(1)(iv) to
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Dated: July 6, 2010.
Peter Tsirigotis,
Director, Sector Policies and Programs
Division.
[FR Doc. 2010–18232 Filed 7–23–10; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
[EPA–HQ–OAR–2010–0133; FRL–9178–3]
Notice of Supplemental Determination
for Renewable Fuels Produced Under
the Final RFS2 Program From Canola
Oil
Environmental Protection
Agency (EPA).
ACTION: Notice of Data Availability
(NODA).
AGENCY:
On March 26, 2010, the
Environmental Protection Agency
published changes to the Renewable
Fuel Standard (RFS) program as
required by the Energy Independence
and Security Act (EISA) of 2007. EISA
increased the volume of renewable fuel
required to be blended into
transportation fuel to 36 billion gallons
by 2022. Furthermore, the Act
established new eligibility requirements
for four types of renewable fuel, each
with their own annual volume
mandates. The eligibility requirements
include minimum lifecycle greenhouse
gas (GHG) reduction thresholds for each
type of renewable fuel. EPA conducted
lifecycle GHG analyses for a number of
biofuel feedstocks and production
pathways as part of its March 26, 2010
final rule but, as indicated in the final
rule, we did not have time to complete
all the planned lifecycle GHG
assessments for several specific
renewable fuel pathways. Since the final
rule, we have completed an assessment
for an additional renewable fuel
pathway, canola oil biodiesel. This
Notice of Data Availability provides
interested parties with information and
an opportunity to comment on our
proposed lifecycle analysis of canola oil
biodiesel.
DATES: Comments must be received on
or before August 25, 2010.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
OAR–2010–0133, by one of the
following methods:
• https://www.regulations.gov: Follow
the on-line instructions for submitting
comments.
• E-mail: asdinfo@epa.gov.
• Mail: Air and Radiation Docket and
Information Center, Environmental
Protection Agency, Mailcode: 2822T,
SUMMARY:
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1200 Pennsylvania Ave., NW.,
Washington, DC 20460.
• Hand Delivery: Air and Radiation
Docket and Information Center, EPA/
DC, EPA West, Room 3334, 1301
Constitution Ave., NW., Washington DC
20004. Such deliveries are only
accepted during the Docket’s normal
hours of operation, and special
arrangements should be made for
deliveries of boxed information.
Instructions: Direct your comments to
Docket ID No. EPA-HQ-OAR–2010–
0133. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through https://
www.regulations.gov or
asdinfo@epa.gov. The https://
www.regulations.gov Web site is an
‘‘anonymous access’’ system, which
means EPA will not know your identity
or contact information unless you
provide it in the body of your comment.
If you send an e-mail comment directly
to EPA without going through https://
www.regulations.gov your e-mail
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, 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 EPA
cannot read your comment due to
technical difficulties and cannot contact
you for clarification, EPA may not be
able to consider your comment.
Electronic files should avoid the use of
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viruses. For additional information
about EPA’s public docket visit the EPA
Docket Center homepage at https://
www.epa.gov/epahome/dockets.htm.
• Docket: All documents in the
docket are listed in the https://
www.regulations.gov index. Although
listed in the index, some information is
not publicly available, e.g., CBI or other
information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
will be publicly available only in hard
copy. Publicly available docket
materials are available either
electronically in https://
www.regulations.gov or in hard copy at
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the Air and Radiation Docket and
Information Center, EPA/DC, EPA West,
Room 3334, 1301 Constitution Ave.,
NW., Washington, DC 20004. The Public
Reading Room is open from 8:30 a.m. to
4:30 p.m., Monday through Friday,
excluding legal holidays. The telephone
number for the Public Reading Room is
(202) 566–1744, and the telephone
number for the Air Docket is (202) 566–
1742.
FOR FURTHER INFORMATION CONTACT:
Doris Wu, Office of Transportation and
Air Quality, Transportation and Climate
Division, Environmental Protection
Agency, 2000 Traverwood Drive, Ann
Arbor, MI 48105; telephone number:
734–214–4923; fax number: 734–214–
4958; e-mail address: wu.doris@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this action apply to me?
Entities potentially affected by this
action are those involved with the
production, distribution, and sale of
transportation fuels, including gasoline
and diesel fuel or renewable fuels such
as ethanol and biodiesel. Regulated
categories include:
This table is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
regulated by the RFS2 program. This
table lists the types of entities that EPA
is now aware of that could potentially
be regulated under the program. To
determine whether your activities
would be regulated, you should
carefully examine the applicability
criteria in 40 CFR part 80, Subpart M.
If you have any questions regarding the
applicability of this action to a
particular entity, consult the person
listed in the preceding section.
B. What should I consider as I prepare
my comments for EPA?
1. Submitting CBI. Do not submit this
information to EPA through https://
www.regulations.gov or e-mail. Clearly
mark the part or all of the information
that you claim to be CBI. For CBI
information in a disk or CD ROM that
you mail to EPA, mark the outside of the
disk or CD ROM as CBI and then
identify electronically within the disk or
CD ROM the specific information that is
claimed as CBI. In addition to one
complete version of the comment that
includes information claimed as CBI, a
copy of the comment that does not
contain the information claimed as CBI
must be submitted for inclusion in the
public docket. Information so marked
will not be disclosed except in
accordance with procedures set forth in
40 CFR part 2.
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2. Tips for Preparing Your Comments.
When submitting comments, remember
to:
• Identify the rulemaking by docket
number and other identifying
information (subject heading, Federal
Register date and page number).
• Follow directions—The agency may
ask you to respond to specific questions
or organize comments by referencing a
Code of Federal Regulations (CFR) part
or section number.
• Explain why you agree or disagree;
suggest alternatives and substitute
language for your requested changes.
• Describe any assumptions and
provide any technical information and/
or data that you used.
• If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow for it to be reproduced.
• Provide specific examples to
illustrate your concerns, and suggest
alternatives.
• Explain your views as clearly as
possible, avoiding the use of profanity
or personal threats.
• Make sure to submit your
comments by the comment period
deadline identified.
II. Background on Lifecycle GHG
Threshold Determinations
A. Methodology
1. Scope of Analysis
On March 26, 2010, the
Environmental Protection Agency (EPA)
published changes to the Renewable
Fuel Standard program as required by
the Energy Independence and Security
Act (EISA) of 2007. This rulemaking is
commonly referred to as the ‘‘RFS2’’
final rule. As part of the RFS2 final rule
we analyzed various categories of
biofuels to determine if the complete
lifecycle emissions associated with the
production, distribution, and use of
those fuels met minimum lifecycle
greenhouse gas reduction thresholds as
specified by EISA (i.e., 60% for
cellulosic biofuel, 50% for biomassbased diesel and advanced biofuel, and
20% for other renewable fuels). Our
final rule had focused our lifecycle
analyses on fuels that were anticipated
to contribute relatively large volumes of
renewable fuel by 2022, and thus did
not cover all fuels that either are
contributing or could potentially
contribute to the program. In the final
RFS2 rule we indicated that we did not
have enough time to complete a
lifecycle analysis for several specific
pathways but would do so this year as
a supplemental to the final rule. Since
the final rule was issued, we have
continued to examine several additional
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pathways not analyzed for the final rule
released in March. This Notice of Data
Availability (‘‘NODA’’) focuses on our
recent modeling of the canola oil
biodiesel pathway. The modeling
approach EPA used in this effort is the
same approach used in the final RFS2
rule for lifecycle analyses of other
biofuels. Refer to the RFS2 final rule
preamble and Regulatory Impact
Analysis (RIA) for further discussion on
our approach.
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2. Models Used
The proposed analysis EPA has
prepared for canola oil biodiesel uses
the same set of models that was used for
the final RFS2 rule: the Forestry and
Agricultural Sector Optimization Model
(FASOM) developed by Texas A&M
University and others and the Food and
Agricultural Policy and Research
Institute international models as
maintained by the Center for
Agricultural and Rural Development
(FAPRI-CARD) at Iowa State University.
For details on the models used refer to
the RFS2 final rule preamble or
Regulatory Impact Analysis. These
documents are available in the docket or
online at https://www.epa.gov/otaq/
fuels/renewablefuels/regulations.htm.
The models require a number of inputs
that are specific to the pathway being
analyzed, including projected yield of
feedstock per acre planted, projected
fertilizer use, energy use in feedstock
processing and energy use in fuel
production. The docket includes
detailed information on model inputs,
assumptions, calculations, and the
results of our proposed modeling for
canola oil biodiesel.
3. Scenarios Modeled
To assess the impacts of an increase
in renewable fuel volume from
business-as-usual (what is likely to have
occurred without EISA), we established
reference and control cases for the RFS2
final rulemaking published in March
2010. The reference cases are
projections of renewable fuel volumes
without the enactment of EISA. The
control cases are projections of the
volumes of renewable fuel that might be
used in the future to comply with the
EISA volume mandates. The final rule
reference case volumes were based on
the Energy Information Administration’s
(EIA) Annual Energy Outlook (AEO)
2007 reference case projections. Our
control case volumes were based on our
projections of a feasible set of fuel types
and feedstocks. Although actual
volumes could be different, we believe
the projections made for our control
cases allow for a reasonable assessment
of the potential GHG impacts per gallon
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of fuel for volumes of renewable fuel
likely resulting from implementation of
the RFS2 program.
For a number of fuel pathways such
as ethanol from corn starch or biodiesel
from soybean oil our reference case
projected the business as usual volumes
from EIA projections for that pathway
which we were then able to compare to
the control case volumes estimated to
increase due to the EISA mandates. This
incremental volume increase in
renewable fuel volume was used to
calculate lifecycle emissions per gallon
or million British Thermal Units
(mmBTU) of renewable fuel. Since our
analysis normalizes the greenhouse gas
emissions impacts on a per BTU basis,
the effect of using different incremental
volumes in our calculations is
minimized.
We based our control case projection
of 200 million gallons of biodiesel from
canola per year in 2022 on a few factors,
including historical volumes, potential
feedstock availability and competitive
uses (e.g., for food or export instead of
for domestic fuel), potential increases in
crop acreage, and potential increases in
crop and conversion yields. Our
assessment is described further in the
inputs and assumptions document that
is available through the docket. Based in
part on consultation with experts at the
United States Department of Agriculture
(USDA) and industry representatives,
we believe that these volumes are
realistic for the purpose of evaluating
the impacts of producing biodiesel from
canola oil. For biodiesel from canola oil,
we do not have reference case
predictions of business as usual
volumes from EIA like we did for other
fuels. We modeled the impact of an
increase of 200 million gallons of
biodiesel from canola per year by 2022
compared to the final RFS2 control case
(from the March 2010 analysis) which
assumed no biodiesel from canola oil.
While we recognize that some canola oil
has historically been used to make
biodiesel for domestic use, this range of
production (zero to 200 million gallons)
covers the range of production likely by
2022. We believe that this modeled
change in canola oil production for
biodiesel provides an assessment of
lifecycle GHG emissions per gallon of
canola biodiesel which reasonably
represents the per gallon impact over
the likely range of canola biodiesel
volumes expected through 2022.
B. Results of Lifecycle Analysis for
Biodiesel From Canola Oil
As with other EPA analyses of fuel
pathways with a significant land use
impact, the proposed analysis for canola
oil biodiesel includes a best estimate as
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well as a range of possible lifecycle
greenhouse gas emission results based
on formal uncertainty analysis
conducted by the Agency.
EPA believes that its analysis of
canola oil biodiesel represents the most
up to date information currently
available on the GHG emissions
associated with each element of the full
fuel lifecycle. Notably the analysis
includes an assessment of uncertainty
for key parameters. The graph included
in the discussion below depicts the
results of our analysis (including the
uncertainty in the modeling) for a
typical pathway for canola oil biodiesel.
We analyzed the lifecycle GHG
emission impacts of producing biodiesel
using canola oil as a feedstock assuming
the same biodiesel production facility
designs and conversion efficiencies as
modeled for biodiesel produced from
soybean oil. Canola oil biodiesel is
produced using the same methods as
soybean oil biodiesel, therefore plant
designs are assumed to not significantly
differ between these two feedstocks.
Refer to the docket for more details on
our key model inputs and assumptions,
e.g., crop yields, biofuel conversion
yields, and agricultural energy use.
These inputs and assumptions are based
on our analysis of peer-reviewed
literature and reflect our consideration
of recommendations of experts within
the canola and biodiesel industries and
those from USDA as well as the experts
at Texas A&M and Iowa State
Universities who have designed the
FASOM and FAPRI models.
As was the case for soybean oil
biodiesel, production technology for
canola oil biodiesel is mature and we
have not projected in our assessment of
canola oil biodiesel any significant
improvements in plant technology;
unanticipated energy saving
improvements would further improve
GHG performance of the fuel pathway.
Additionally, similar to soybean oil
biodiesel production, we assumed that
the co-product glycerin would displace
residual oil as a fuel source on an
energy equivalent basis. This is based
on the assumption that the glycerin
market would be saturated in 2022 and
that glycerin produced from biodiesel
would not displace any additional
petroleum glycerin production.
However, the biodiesel glycerin would
not be a waste and a low value use
would be to use the glycerin as a fuel
source. The fuel source assumed to be
replaced by the glycerin is residual oil.
Figure II–1 shows the results of our
proposed modeling. It shows the
percent difference between lifecycle
GHG emissions for the typical 2022
canola oil biodiesel as compared to the
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renewable biomass, and used to reduce
or replace transportation fuel) specified
in EISA.
The material in the docket includes
detailed information on the assumptions
and modeling inputs used. As was the
case for analyses of other crop-based
biofuels, EPA projected increases in
canola crop yield based on long term
trends. Yield improvement rates
recommended by industry were higher
and were based on recent shorter term
trends. While we have not modeled
what specific impact a higher crop yield
assumption would have on the resulting
lifecycle GHG assessment, higher
projected yields would tend to reduce
land use impacts which could result in
some improvement in projected GHG
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performance of canola biodiesel. EPA
invites comment on all aspects of its
proposed modeling of the canola oil
biodiesel pathway, including all
assumptions made and modeling inputs.
Table II–1 breaks down by stage the
lifecycle GHG emissions for canola oil
biodiesel and the 2005 diesel baseline.
The biodiesel production process
reflected in this table assumes that
natural gas is used for process energy
and accounts for co-product glycerin
displacing residual oil. This table
demonstrates the contribution of each
stage and its relative significance. The
docket also includes pathway analyses
assuming coal or biomass is used
instead of natural gas for process energy.
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petroleum diesel fuel 2005 baseline.
Lifecycle GHG emissions equivalent to
the diesel fuel baseline are represented
on the graph by the zero on the X-axis.
The results for canola biodiesel are that
the midpoint of the range of results is
a 50% reduction in GHG emissions
compared to the diesel fuel baseline.
The 95% confidence interval around
that midpoint results in range of a 20%
reduction to a 75% reduction compared
to the diesel fuel 2005 baseline. These
results, if finalized, would justify
authorizing the generation of biomassbased diesel RINs for fuel produced by
the canola oil biodiesel pathway
modeled, assuming that the fuel meets
the other definitional criteria for
renewable fuel (e.g., produced from
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TABLE II–1—LIFECYCLE GHG EMISSIONS FOR CANOLA OIL BIODIESEL, 2022
[kgCO2e/mmBTU]
Canola oil biodiesel
Fuel type
2005 Diesel
baseline
Net Domestic Agriculture (w/o land use change) ............................................................................................
Net International Agriculture (w/o land use change) .......................................................................................
Domestic Land Use Change ...........................................................................................................................
International Land Use Change, Mean (Low/High) .........................................................................................
Fuel Production ................................................................................................................................................
Fuel and Feedstock Transport ........................................................................................................................
Tailpipe Emissions ...........................................................................................................................................
8
0
3
31 (7/61)
3
2
1
18
*
79
Total Emissions, Mean (Low/High) ..........................................................................................................
48 (25/78)
97
* Emissions included in fuel production stage.
Refer to the docket for more detailed
outputs from our proposed lifecycle
modeling. The docket includes a useful
memorandum which summarizes
relevant materials used for the canola
biodiesel pathways analysis. Described
in the memorandum, for example, are
the input and assumptions document
and detailed results spreadsheets (e.g.,
foreign agricultural impacts, foreign
agricultural energy use, FASOM and
FAPRI model results) used to generate
the results presented above. These
additional materials are also available
through the docket.
Dated: July 13, 2010.
Margo T. Oge,
Director, Office of Transportation & Air
Quality.
[FR Doc. 2010–18227 Filed 7–23–10; 8:45 am]
BILLING CODE 6560–50–P
FEDERAL TRADE COMMISSION
Agency Information Collection
Activities; Proposed Collection;
Comment Request
Request for Comments
Federal Trade Commission
(‘‘FTC’’ or ‘‘Commission’’).
ACTION: Notice.
AGENCY:
The information collection
requirements described below will be
submitted to the Office of Management
and Budget (‘‘OMB’’) for review, as
required by the Paperwork Reduction
Act (‘‘PRA’’). The FTC seeks public
comments on its proposal to extend
through December 31, 2013 the current
OMB clearance for information
collection requirements contained in its
Affiliate Marketing Rule (or ‘‘Rule’’).
That clearance expires on December 31,
2010.
DATES: Comments must be filed by
September 24, 2010.
ADDRESSES: Interested parties are
invited to submit written comments
electronically or in paper form by
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SUMMARY:
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following the instructions in the
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below. Comments in electronic form
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AffiliateMarketingPRA) (and following
the instructions on the web-based form).
Comments filed in paper form should be
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N.W., Washington, DC 20580, in the
manner detailed in the SUPPLEMENTARY
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Requests for additional information
should be addressed to Anthony
Rodriguez, Attorney, Division of Privacy
and Identity Protection, Bureau of
Consumer Protection, Federal Trade
Commission, 600 Pennsylvania Avenue,
N.W., Washington, DC 20580, (202) 3262757.
SUPPLEMENTARY INFORMATION:
Interested parties are invited to
submit written comments. Comments
should refer to ‘‘Affiliate Marketing
Rule: FTC File No. P105411’’ to facilitate
the organization of comments. Please
note that your comment – including
your name and your state – will be
placed on the public record of this
proceeding, including on the publicly
accessible FTC website, at (https://
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Because comments will be made
public, they should not include any
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addition, comments should not include
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Comments containing matter for which
confidential treatment is requested must
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AffiliateMarketingPRA) (and following
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To ensure that the Commission
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E:\FR\FM\26JYN1.SGM
26JYN1
Agencies
[Federal Register Volume 75, Number 142 (Monday, July 26, 2010)]
[Notices]
[Pages 43522-43526]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2010-18227]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
[EPA-HQ-OAR-2010-0133; FRL-9178-3]
Notice of Supplemental Determination for Renewable Fuels Produced
Under the Final RFS2 Program From Canola Oil
AGENCY: Environmental Protection Agency (EPA).
ACTION: Notice of Data Availability (NODA).
-----------------------------------------------------------------------
SUMMARY: On March 26, 2010, the Environmental Protection Agency
published changes to the Renewable Fuel Standard (RFS) program as
required by the Energy Independence and Security Act (EISA) of 2007.
EISA increased the volume of renewable fuel required to be blended into
transportation fuel to 36 billion gallons by 2022. Furthermore, the Act
established new eligibility requirements for four types of renewable
fuel, each with their own annual volume mandates. The eligibility
requirements include minimum lifecycle greenhouse gas (GHG) reduction
thresholds for each type of renewable fuel. EPA conducted lifecycle GHG
analyses for a number of biofuel feedstocks and production pathways as
part of its March 26, 2010 final rule but, as indicated in the final
rule, we did not have time to complete all the planned lifecycle GHG
assessments for several specific renewable fuel pathways. Since the
final rule, we have completed an assessment for an additional renewable
fuel pathway, canola oil biodiesel. This Notice of Data Availability
provides interested parties with information and an opportunity to
comment on our proposed lifecycle analysis of canola oil biodiesel.
DATES: Comments must be received on or before August 25, 2010.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
OAR-2010-0133, by one of the following methods:
https://www.regulations.gov: Follow the on-line
instructions for submitting comments.
E-mail: asdinfo@epa.gov.
Mail: Air and Radiation Docket and Information Center,
Environmental Protection Agency, Mailcode: 2822T,
[[Page 43523]]
1200 Pennsylvania Ave., NW., Washington, DC 20460.
Hand Delivery: Air and Radiation Docket and Information
Center, EPA/DC, EPA West, Room 3334, 1301 Constitution Ave., NW.,
Washington DC 20004. Such deliveries are only accepted during the
Docket's normal hours of operation, and special arrangements should be
made for deliveries of boxed information.
Instructions: Direct your comments to Docket ID No. EPA-HQ-OAR-
2010-0133. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
https://www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI or otherwise protected through https://www.regulations.gov or asdinfo@epa.gov. The https://www.regulations.gov
Web site is an ``anonymous access'' system, which means EPA will not
know your identity or contact information unless you provide it in the
body of your comment. If you send an e-mail comment directly to EPA
without going through https://www.regulations.gov your e-mail 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, 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 EPA cannot read your comment due to
technical difficulties and cannot contact you for clarification, 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. For additional information about EPA's public
docket visit the EPA Docket Center homepage at https://www.epa.gov/epahome/dockets.htm.
Docket: All documents in the docket are listed in the
https://www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, will be publicly available only in hard copy.
Publicly available docket materials are available either electronically
in https://www.regulations.gov or in hard copy at the Air and Radiation
Docket and Information Center, EPA/DC, EPA West, Room 3334, 1301
Constitution Ave., NW., Washington, DC 20004. The Public Reading Room
is open from 8:30 a.m. to 4:30 p.m., Monday through Friday, excluding
legal holidays. The telephone number for the Public Reading Room is
(202) 566-1744, and the telephone number for the Air Docket is (202)
566-1742.
FOR FURTHER INFORMATION CONTACT: Doris Wu, Office of Transportation and
Air Quality, Transportation and Climate Division, Environmental
Protection Agency, 2000 Traverwood Drive, Ann Arbor, MI 48105;
telephone number: 734-214-4923; fax number: 734-214-4958; e-mail
address: wu.doris@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this action apply to me?
Entities potentially affected by this action are those involved
with the production, distribution, and sale of transportation fuels,
including gasoline and diesel fuel or renewable fuels such as ethanol
and biodiesel. Regulated categories include:
This table is not intended to be exhaustive, but rather provides a
guide for readers regarding entities likely to be regulated by the RFS2
program. This table lists the types of entities that EPA is now aware
of that could potentially be regulated under the program. To determine
whether your activities would be regulated, you should carefully
examine the applicability criteria in 40 CFR part 80, Subpart M. If you
have any questions regarding the applicability of this action to a
particular entity, consult the person listed in the preceding section.
B. What should I consider as I prepare my comments for EPA?
1. Submitting CBI. Do not submit this information to EPA through
https://www.regulations.gov or e-mail. Clearly mark the part or all of
the information that you claim to be CBI. For CBI information in a disk
or CD ROM that you mail to EPA, mark the outside of the disk or CD ROM
as CBI and then identify electronically within the disk or CD ROM the
specific information that is claimed as CBI. In addition to one
complete version of the comment that includes information claimed as
CBI, a copy of the comment that does not contain the information
claimed as CBI must be submitted for inclusion in the public docket.
Information so marked will not be disclosed except in accordance with
procedures set forth in 40 CFR part 2.
2. Tips for Preparing Your Comments. When submitting comments,
remember to:
Identify the rulemaking by docket number and other
identifying information (subject heading, Federal Register date and
page number).
Follow directions--The agency may ask you to respond to
specific questions or organize comments by referencing a Code of
Federal Regulations (CFR) part or section number.
Explain why you agree or disagree; suggest alternatives
and substitute language for your requested changes.
Describe any assumptions and provide any technical
information and/or data that you used.
If you estimate potential costs or burdens, explain how
you arrived at your estimate in sufficient detail to allow for it to be
reproduced.
Provide specific examples to illustrate your concerns, and
suggest alternatives.
Explain your views as clearly as possible, avoiding the
use of profanity or personal threats.
Make sure to submit your comments by the comment period
deadline identified.
II. Background on Lifecycle GHG Threshold Determinations
A. Methodology
1. Scope of Analysis
On March 26, 2010, the Environmental Protection Agency (EPA)
published changes to the Renewable Fuel Standard program as required by
the Energy Independence and Security Act (EISA) of 2007. This
rulemaking is commonly referred to as the ``RFS2'' final rule. As part
of the RFS2 final rule we analyzed various categories of biofuels to
determine if the complete lifecycle emissions associated with the
production, distribution, and use of those fuels met minimum lifecycle
greenhouse gas reduction thresholds as specified by EISA (i.e., 60% for
cellulosic biofuel, 50% for biomass-based diesel and advanced biofuel,
and 20% for other renewable fuels). Our final rule had focused our
lifecycle analyses on fuels that were anticipated to contribute
relatively large volumes of renewable fuel by 2022, and thus did not
cover all fuels that either are contributing or could potentially
contribute to the program. In the final RFS2 rule we indicated that we
did not have enough time to complete a lifecycle analysis for several
specific pathways but would do so this year as a supplemental to the
final rule. Since the final rule was issued, we have continued to
examine several additional
[[Page 43524]]
pathways not analyzed for the final rule released in March. This Notice
of Data Availability (``NODA'') focuses on our recent modeling of the
canola oil biodiesel pathway. The modeling approach EPA used in this
effort is the same approach used in the final RFS2 rule for lifecycle
analyses of other biofuels. Refer to the RFS2 final rule preamble and
Regulatory Impact Analysis (RIA) for further discussion on our
approach.
2. Models Used
The proposed analysis EPA has prepared for canola oil biodiesel
uses the same set of models that was used for the final RFS2 rule: the
Forestry and Agricultural Sector Optimization Model (FASOM) developed
by Texas A&M University and others and the Food and Agricultural Policy
and Research Institute international models as maintained by the Center
for Agricultural and Rural Development (FAPRI-CARD) at Iowa State
University. For details on the models used refer to the RFS2 final rule
preamble or Regulatory Impact Analysis. These documents are available
in the docket or online at https://www.epa.gov/otaq/fuels/renewablefuels/regulations.htm. The models require a number of inputs
that are specific to the pathway being analyzed, including projected
yield of feedstock per acre planted, projected fertilizer use, energy
use in feedstock processing and energy use in fuel production. The
docket includes detailed information on model inputs, assumptions,
calculations, and the results of our proposed modeling for canola oil
biodiesel.
3. Scenarios Modeled
To assess the impacts of an increase in renewable fuel volume from
business-as-usual (what is likely to have occurred without EISA), we
established reference and control cases for the RFS2 final rulemaking
published in March 2010. The reference cases are projections of
renewable fuel volumes without the enactment of EISA. The control cases
are projections of the volumes of renewable fuel that might be used in
the future to comply with the EISA volume mandates. The final rule
reference case volumes were based on the Energy Information
Administration's (EIA) Annual Energy Outlook (AEO) 2007 reference case
projections. Our control case volumes were based on our projections of
a feasible set of fuel types and feedstocks. Although actual volumes
could be different, we believe the projections made for our control
cases allow for a reasonable assessment of the potential GHG impacts
per gallon of fuel for volumes of renewable fuel likely resulting from
implementation of the RFS2 program.
For a number of fuel pathways such as ethanol from corn starch or
biodiesel from soybean oil our reference case projected the business as
usual volumes from EIA projections for that pathway which we were then
able to compare to the control case volumes estimated to increase due
to the EISA mandates. This incremental volume increase in renewable
fuel volume was used to calculate lifecycle emissions per gallon or
million British Thermal Units (mmBTU) of renewable fuel. Since our
analysis normalizes the greenhouse gas emissions impacts on a per BTU
basis, the effect of using different incremental volumes in our
calculations is minimized.
We based our control case projection of 200 million gallons of
biodiesel from canola per year in 2022 on a few factors, including
historical volumes, potential feedstock availability and competitive
uses (e.g., for food or export instead of for domestic fuel), potential
increases in crop acreage, and potential increases in crop and
conversion yields. Our assessment is described further in the inputs
and assumptions document that is available through the docket. Based in
part on consultation with experts at the United States Department of
Agriculture (USDA) and industry representatives, we believe that these
volumes are realistic for the purpose of evaluating the impacts of
producing biodiesel from canola oil. For biodiesel from canola oil, we
do not have reference case predictions of business as usual volumes
from EIA like we did for other fuels. We modeled the impact of an
increase of 200 million gallons of biodiesel from canola per year by
2022 compared to the final RFS2 control case (from the March 2010
analysis) which assumed no biodiesel from canola oil. While we
recognize that some canola oil has historically been used to make
biodiesel for domestic use, this range of production (zero to 200
million gallons) covers the range of production likely by 2022. We
believe that this modeled change in canola oil production for biodiesel
provides an assessment of lifecycle GHG emissions per gallon of canola
biodiesel which reasonably represents the per gallon impact over the
likely range of canola biodiesel volumes expected through 2022.
B. Results of Lifecycle Analysis for Biodiesel From Canola Oil
As with other EPA analyses of fuel pathways with a significant land
use impact, the proposed analysis for canola oil biodiesel includes a
best estimate as well as a range of possible lifecycle greenhouse gas
emission results based on formal uncertainty analysis conducted by the
Agency.
EPA believes that its analysis of canola oil biodiesel represents
the most up to date information currently available on the GHG
emissions associated with each element of the full fuel lifecycle.
Notably the analysis includes an assessment of uncertainty for key
parameters. The graph included in the discussion below depicts the
results of our analysis (including the uncertainty in the modeling) for
a typical pathway for canola oil biodiesel.
We analyzed the lifecycle GHG emission impacts of producing
biodiesel using canola oil as a feedstock assuming the same biodiesel
production facility designs and conversion efficiencies as modeled for
biodiesel produced from soybean oil. Canola oil biodiesel is produced
using the same methods as soybean oil biodiesel, therefore plant
designs are assumed to not significantly differ between these two
feedstocks. Refer to the docket for more details on our key model
inputs and assumptions, e.g., crop yields, biofuel conversion yields,
and agricultural energy use. These inputs and assumptions are based on
our analysis of peer-reviewed literature and reflect our consideration
of recommendations of experts within the canola and biodiesel
industries and those from USDA as well as the experts at Texas A&M and
Iowa State Universities who have designed the FASOM and FAPRI models.
As was the case for soybean oil biodiesel, production technology
for canola oil biodiesel is mature and we have not projected in our
assessment of canola oil biodiesel any significant improvements in
plant technology; unanticipated energy saving improvements would
further improve GHG performance of the fuel pathway. Additionally,
similar to soybean oil biodiesel production, we assumed that the co-
product glycerin would displace residual oil as a fuel source on an
energy equivalent basis. This is based on the assumption that the
glycerin market would be saturated in 2022 and that glycerin produced
from biodiesel would not displace any additional petroleum glycerin
production. However, the biodiesel glycerin would not be a waste and a
low value use would be to use the glycerin as a fuel source. The fuel
source assumed to be replaced by the glycerin is residual oil.
Figure II-1 shows the results of our proposed modeling. It shows
the percent difference between lifecycle GHG emissions for the typical
2022 canola oil biodiesel as compared to the
[[Page 43525]]
petroleum diesel fuel 2005 baseline. Lifecycle GHG emissions equivalent
to the diesel fuel baseline are represented on the graph by the zero on
the X-axis. The results for canola biodiesel are that the midpoint of
the range of results is a 50% reduction in GHG emissions compared to
the diesel fuel baseline. The 95% confidence interval around that
midpoint results in range of a 20% reduction to a 75% reduction
compared to the diesel fuel 2005 baseline. These results, if finalized,
would justify authorizing the generation of biomass-based diesel RINs
for fuel produced by the canola oil biodiesel pathway modeled, assuming
that the fuel meets the other definitional criteria for renewable fuel
(e.g., produced from renewable biomass, and used to reduce or replace
transportation fuel) specified in EISA.
The material in the docket includes detailed information on the
assumptions and modeling inputs used. As was the case for analyses of
other crop-based biofuels, EPA projected increases in canola crop yield
based on long term trends. Yield improvement rates recommended by
industry were higher and were based on recent shorter term trends.
While we have not modeled what specific impact a higher crop yield
assumption would have on the resulting lifecycle GHG assessment, higher
projected yields would tend to reduce land use impacts which could
result in some improvement in projected GHG performance of canola
biodiesel. EPA invites comment on all aspects of its proposed modeling
of the canola oil biodiesel pathway, including all assumptions made and
modeling inputs.
Table II-1 breaks down by stage the lifecycle GHG emissions for
canola oil biodiesel and the 2005 diesel baseline. The biodiesel
production process reflected in this table assumes that natural gas is
used for process energy and accounts for co-product glycerin displacing
residual oil. This table demonstrates the contribution of each stage
and its relative significance. The docket also includes pathway
analyses assuming coal or biomass is used instead of natural gas for
process energy.
[GRAPHIC] [TIFF OMITTED] TN26JY10.081
[[Page 43526]]
Table II-1--Lifecycle GHG Emissions for Canola Oil Biodiesel, 2022
[kgCO2e/mmBTU]
------------------------------------------------------------------------
Canola oil 2005 Diesel
Fuel type biodiesel baseline
------------------------------------------------------------------------
Net Domestic Agriculture (w/o land 8
use change)........................
Net International Agriculture (w/o 0
land use change)...................
Domestic Land Use Change............ 3
International Land Use Change, Mean 31 (7/61)
(Low/High).........................
Fuel Production..................... 3 18
Fuel and Feedstock Transport........ 2 *
Tailpipe Emissions.................. 1 79
-----------------------------------
Total Emissions, Mean (Low/High) 48 (25/78) 97
------------------------------------------------------------------------
* Emissions included in fuel production stage.
Refer to the docket for more detailed outputs from our proposed
lifecycle modeling. The docket includes a useful memorandum which
summarizes relevant materials used for the canola biodiesel pathways
analysis. Described in the memorandum, for example, are the input and
assumptions document and detailed results spreadsheets (e.g., foreign
agricultural impacts, foreign agricultural energy use, FASOM and FAPRI
model results) used to generate the results presented above. These
additional materials are also available through the docket.
Dated: July 13, 2010.
Margo T. Oge,
Director, Office of Transportation & Air Quality.
[FR Doc. 2010-18227 Filed 7-23-10; 8:45 am]
BILLING CODE 6560-50-P