Petition for Writ of Certiorari — Valero Energy Corporation, et al., Petitioners v. Environmental Protection Agency
Supreme Court briefDec 30, 2019
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No. 19-_____
IN THE
Supreme Court of the United States
VALERO ENERGY CORPORATION AND
AMERICAN FUEL & PETROCHEMICAL MANUFACTURERS,
Petitioners,
v.
ENVIRONMENTAL PROTECTION AGENCY,
Respondent.
On Petition for a Writ of Certiorari
to the United States Court of Appeals
for the District of Columbia Circuit
PETITION FOR A WRIT OF CERTIORARI
VOLUME II OF II
CLARA M. POFFENBERGER
CLARA POFFENBERGER
ENVIRONMENTAL LAW
AND POLICY, LLC
2933 Fairhill Road
Fairfax, Virginia 22031
(703) 231-5251
EVAN A. YOUNG
Counsel of Record
ELLEN SPRINGER
JOSHUA MORROW
BAKER BOTTS L.L.P.
98 San Jacinto Boulevard
Suite 1500
Austin, Texas 78701
(512) 322-2506
evan.young@bakerbotts.com
Counsel for Petitioner Valero Energy Corporation
(additional counsel on inside front cover)
WILSON-EPES PRINTING CO., INC. – (202) 789-0096 – W ASHINGTON, D.C. 20002
SAMARA L. KLINE
BAKER BOTTS L.L.P.
2001 Ross Avenue
Dallas, Texas 75201
(214) 953-6825
MEGAN H. BERGE
BAKER BOTTS L.L.P.
The Warner
1299 Pennsylvania Ave., N.W.
Washington, D.C. 20004
(202) 639-1308
BRITTANY M. PEMBERTON
BRACEWELL LLP
2001 M Street N.W.
Suite 900
Washington, D.C. 20036
(202) 828-1708
Counsel for Petitioner
Valero Energy Corporation
RICHARD MOSKOWITZ
AMERICAN FUEL &
PETROCHEMICAL
MANUFACTURERS
1800 M Street, NW
Suite 900 North
Washington, D.C. 20036
(202) 457-0480
Counsel for Petitioner
American Fuel &
Petrochemical Manufacturers
TABLE OF CONTENTS
VOLUME I
Appendix A – Opinion of the D.C. Circuit
(August 30, 2019) ................................................................ 1a
Appendix B – Opinion of the D.C. Circuit
(September 6, 2019) .......................................................... 91a
Appendix C – Statutory Provisions Involved .............. 156a
VOLUME II
Appendix D – U.S. Environmental Protection
Agency, Renewable Fuel Standard Program Standards For 2017 And Biomass-Based Diesel
Volume For 2018: Response To Comments,
EPA-420-R-16-019 (November 2016) ........................... 187a
Appendix E – U.S. Environmental Protection
Agency, Renewable Fuel Standard Program:
Standards for 2017 and Biomass-Based Diesel
Volume for 2018, 81 Fed. Reg. 89,746
(December 12, 2016) (“2017 Rule”) ............................... 189a
Appendix F – U.S. Environmental Protection
Agency, Denial of Petitions for Rulemaking to
Change the RFS Point of Obligation,
EPA-420-R-17-008 (November 2017) ........................... 356a
Appendix G – U.S. Environmental Protection
Agency, Notice of Denial of Petitions for Rulemaking To Change the RFS Point of Obligation,
82 Fed. Reg. 56,779 (November 30, 2017) .................... 531a
Appendix H – U.S. Environmental Protection
Agency, Renewable Fuel Standard Program:
Standards for 2018 and Biomass-Based Diesel
Volume for 2019 (Proposed Rule) 82 Fed. Reg.
34,206 (July 21, 2017) ..................................................... 538a
(i)
ii
Appendix I – U.S. Environmental Protection
Agency, Renewable Fuel Standard Program:
Standards for 2018 and Biomass-Based Diesel
Volume for 2019; Availability of Supplemental
Information and Request for Further Comment,
82 Fed. Reg. 46,174 (October 4, 2017) .......................... 541a
Appendix J – U.S. Environmental Protection
Agency, Renewable Fuel Standard Program Standards for 2018 and Biomass-Based Diesel
Volume for 2019: Response to Comments,
EPA-420-R-17-007 (December 2017) ........................... 550a
Appendix K – U.S. Environmental Protection
Agency, Renewable Fuel Standard Program:
Standards for 2018 and Biomass-Based Diesel
Volume for 2019, 82 Fed. Reg. 58,486
(December 12, 2017) (“2018 Rule”) ............................... 552a
187a
APPENDIX D
U.S. ENVIRONMENTAL
PROTECTION AGENCY
OFFICE OF TRANSPORTATION
AND AIR QUALITY
ASSESSMENT AND STANDARDS DIVISION
————
EPA-420-R-16-019
————
Renewable Fuel Standard
Program Standards For 2017
And Biomass-Based Diesel
Volume For 2018:
Response To Comments
————
NOVEMBER 2016
————
[Content Omitted]
In the proposed rule, EPA did not propose any
changes to the definition of an obligated party, nor
did we specifically seek comment on this issue. EPA
received comments requesting that we change the point
of obligation in the RFS program primarily from parties that are obligated under the current regulations.
We also received comments from several parties opposed
to changing the point of obligation. These comments
are beyond the scope of this rulemaking.
In a separate action EPA has proposed to deny the
petitions we have received to change the point of obligation in the RFS program. EPA has opened a public
188a
docket (EPA-HQ-OAR-2016-0544) to receive comments
on our proposed denial of these petitions.72 Our proposed response to the petitions we have received,
together with the petitions, comments received to-date
on the petitions, and EPA’s draft analysis can also be
found in this docket.
[Content Omitted]
72
The EPA Administrator signed the Proposed Denial of
Petitions for Rulemaking to Change the RFS Point of Obligation
on November 10, 2016. More information about this proposed
rule can be found at https://www.epa.gov/renewable-fuel-standardprogram/response-petitions-reconsideration-rfs2-rule-changepoint-obligation
189a
APPENDIX E
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 80
————
[EPA–HQ–OAR–2016–0004; FRL–9955–84–OAR]
RIN 2060–AS72
————
Renewable Fuel Standard Program:
Standards for 2017 and Biomass-Based
Diesel Volume for 2018
————
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule [December 12, 2016].
SUMMARY: Under section 211 of the Clean Air Act,
the Environmental Protection Agency (EPA) is required
to set renewable fuel percentage standards every year.
This action establishes the annual percentage standards for cellulosic biofuel, biomass-based diesel, advanced biofuel, and total renewable fuel that apply to
all motor vehicle gasoline and diesel produced or imported in the year 2017. Relying on statutory authority
that is available when projected cellulosic biofuel production volumes are less than the applicable volume
specified in the statute, the EPA is setting volume
requirements for cellulosic biofuel, advanced biofuel,
and total renewable fuel that are below the statutory
applicable volumes, but which are nevertheless significantly higher than past requirements. The final rule
also establishes the four percentage standards applicable to obligated parties, namely producers and
importer of gasoline and diesel, based on the corresponding volume requirements. The final standards
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are expected to continue driving the market to overcome constraints in renewable fuel distribution infrastructure, which in turn is expected to lead to substantial growth over time in the production and use of
renewable fuels. In this action, we are also establishing the applicable volume of biomass-based diesel for
2018.
DATES: This final rule is effective on February 10,
2017.
ADDRESSES: The EPA has established a docket for
this action under Docket ID No. EPA–HQ–OAR–
2016–0004. All documents in the docket are listed on
the http://www.regulations.gov Web site. 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, is not placed on the Internet and will be publicly available only in hard copy
form. Publicly available docket materials are available
electronically through http:// www.regulations.gov.
FOR FURTHER INFORMATION CONTACT:
Julia MacAllister, Office of Transportation and Air
Quality, Assessment and Standards Division, Environmental Protection Agency, 2000 Traverwood Drive,
Ann Arbor, MI 48105; telephone number: 734–214–
4131; email address: macallister.julia@epa.gov.
SUPPLEMENTARY INFORMATION:
Entities potentially affected by this final rule are those
involved with the production, distribution, and sale of
transportation fuels, including gasoline and diesel fuel
or renewable fuels such as ethanol, biodiesel, renewable diesel, and biogas. Potentially regulated categories
include:
191a
1,2
This table is not intended to be exhaustive, but
rather provides a guide for readers regarding entities
likely to be regulated by this final action. This table
lists the types of entities that EPA is now aware could
potentially be regulated by this final action. Other
types of entities not listed in the table could also be
regulated. To determine whether your entity would be
regulated by this final action, you should carefully
examine the applicability criteria in 40 CFR part 80.
If you have any questions regarding the applicability
of this final action to a particular entity, consult the
person listed in the FOR FURTHER INFORMATION
CONTACT section.
1
North American Industry Classification System (NAICS).
2
Standard Industrial Classification (SIC) system code.
192a
Outline of This Preamble
I. Executive Summary
A. Purpose of This Action
B. Summary of Major Provisions in This
Action
1. Approach to Setting Volume
Requirements
2. Cellulosic Biofuel
3. Advanced Biofuel
4. Total Renewable Fuel
5. Biomass-Based Diesel
6. Annual Percentage Standards
7. Assessment of Aggregate
Compliance
II. Authority and Need for Waiver of Statutory Applicable Volumes
A. Statutory Authorities for Reducing
Volume Targets
1. Cellulosic Waiver Authority
2. General Waiver Authority
3. General Comments Related to
Waiver Authorities
B. Treatment of Carryover RINs
1. Updated Projection of Carryover
RIN Volume
2. EPA’s Decision
III. Cellulosic Biofuel Volume for 2017
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A. Statutory Requirements
B. Cellulosic Biofuel Industry Assessment
1. Potential Domestic Producers
2. Potential Foreign Sources of Cellulosic Biofuel
3. Summary of Volume Projections
for Individual Companies
C. Projection From the Energy Information Administration
D. Cellulosic Biofuel Volume for 2017
IV. Advanced Biofuel Volume for 2017
A. Volumetric Limitation on Use of the
Cellulosic Waiver Authority
B. Determination of Reasonably Attainable and Appropriate Volumes
1. Imported Sugarcane Ethanol
2. Biodiesel and Renewable Diesel
3. Other Advanced Biofuel
4. Total Advanced Biofuel
V. Total Renewable Fuel Volume for 2017
A. Volumetric Limitation on Use of the
Cellulosic Waiver Authority
B. Assessing Adequacy of Supply
1. Ethanol
i. E0
ii. E15
iii. E85
194a
iv. Total Ethanol
2. Biodiesel and Renewable Diesel
i. Feedstock Availability
ii. Biodiesel and Renewable Diesel
Production Capacity
iii. Biodiesel and Renewable Diesel
Import Capacity
iv. Biodiesel and Renewable Diesel
Distribution Capacity
v. Biodiesel and Renewable Diesel
Retail Infrastructure Capacity
vi. Biodiesel and Renewable Diesel
Consumption Capacity
vii. Biodiesel and Renewable Diesel
Consumer Response
viii. Projected Supply of Biodiesel
and Renewable Diesel in 2017
3. Total Renewable Fuel Supply
C. Market Responses to the Advanced
Biofuel and Total Renewable Fuel Volume Requirements
D. Impacts of 2017 Standards on Costs
VI. Biomass-Based Diesel Volume for 2018
A. Statutory Requirements
B. Determination of Applicable Volume
of Biomass-Based Diesel
1. BBD Production and Compliance
Through 2015
195a
2. Interaction Between BBD and Advanced Biofuel Standards
3. BBD Volume for 2018
C. Consideration of Statutory Factors for
2018
VII. Percentage Standards for 2017
A. Calculation of Percentage Standards
B. Small Refineries and Small Refiners
C. Final Standards
VIII. Assessment of Aggregate Compliance
A. Assessment of the Domestic Aggregate
Compliance Approach
B. Assessment of the Canadian Aggregate
Compliance Approach
IX. Public Participation
X. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation
and Regulatory Review
B. Paperwork Reduction Act (PRA)
C. Regulatory Flexibility Act (RFA)
D. Unfunded
(UMRA)
Mandates
Reform
Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
196a
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
H. Executive Order 13211: Actions Concerning Regulations That Significantly
Affect Energy Supply, Distribution, or
Use
I. National Technology Transfer and
Advancement Act (NTTAA)
J. Executive Order 12898: Federal Actions To Address Environmental Justice in Minority Populations, and LowIncome Populations
K. Congressional Review Act (CRA)
XI. Statutory Authority
197a
I. Executive Summary
The Renewable Fuel Standard (RFS) program began
in 2006 pursuant to the requirements in Clean Air Act
(CAA) section 211(o) that were added through the
Energy Policy Act of 2005 (EPAct). The statutory
requirements for the RFS program were subsequently
modified through the Energy Independence and Security Act of 2007 (EISA), resulting in the publication of
major revisions to the regulatory requirements on
March 26, 2010.1 EISA’s stated goals include moving
the United States toward “greater energy independence and security, to increase the production of clean
renewable fuels.” Today, nearly all of the approximately 142 billion gallons of gasoline used for transportation purposes contains 10 percent ethanol (E10),
and a substantial portion of diesel fuel contains biodiesel.
Renewable fuels represent an opportunity for the U.S.
to move away from fossil fuels towards a set of lower
lifecycle GHG transportation fuels, and the RFS program provides incentives for these lower lifecycle GHG
fuels to grow and compete in the market. While renewable fuels include non-advanced (conventional) corn
starch ethanol, which is the predominant renewable
fuel in use to date, Congress envisioned the majority
of growth from 2014 forward to come from advanced
biofuels, as the conventional volumes remain constant
in the statutory volume tables starting in 2015 while
the advanced volumes continue to grow.2
1
2
75 FR 14670, March 26, 2010.
In this document we follow the common practice of using the
term “conventional” renewable fuel to mean any renewable fuel
that is not an advance biofuel.
198a
The statute includes annual volume targets, and
requires EPA to translate those volume targets (or
alternative volume requirements established by EPA
in accordance with statutory waiver authorities) into
compliance obligations that refiners and importers must
meet every year. In this action, we are establishing the
annual percentage standards for cellulosic biofuel,
biomass-based diesel, advanced biofuel, and total renewable fuel that would apply to all gasoline and diesel
produced or imported in 2017. We are also establishing
the applicable volume of biomass-based diesel for 2018.
The standards we are setting are designed to
achieve the Congressional intent of increasing renewable fuel use over time in order to reduce lifecycle GHG
emissions of transportation fuels and increase energy
security, while at the same time accounting for the
real-world challenges that have slowed progress
toward these goals. Those challenges have made the
volume targets established by Congress for 2017 beyond
reach for all fuel categories other than biomass-based
diesel (BBD), for which the statute specifies only a
minimum requirement of 1.0 billion gallons. In setting
these standards for 2017, we have used the cellulosic
waiver authority provision provided by Congress to
establish volume requirements that will be lower than
the statutory targets for fuels other than biomass-based
diesel, but nevertheless represent significant growth
from past years.
The 2017 volume requirements for advanced biofuel
and total renewable fuel are higher than the levels we
proposed in the NPRM, reflecting our assessment of
updated information and a review of comments
received. We are also finalizing the proposed volume
requirement for BBD for 2018. This BBD volume
requirement will continue to provide support for the
199a
BBD industry, and we expect that larger volumes of
this fuel type are likely to be used to comply with the
advanced biofuel requirement. The final volume requirements are shown in Table I–1 below. These final volumes, when considered together with the volumes established over the past several years of the RFS program,
indicate that the RFS program is working to deliver
steady, ambitious growth in the total amount of renewable fuel produced and used in the United States,
consistent with Congressional intent.
TABLE I–1—PROPOSED AND FINAL
VOLUME REQUIREMENTSa
2017
2018
Proposed Final Proposed Final
Cellulosic biofuel
(million gallons)
Biomass-based
diesel (billion
gallons)
Advanced biofuel
(billion gallons)
Renewable fuel
(billion gallons)
312
311
n/a
n/a
b
2.0
b
2.0
2.1
2.1
4.0
4.28
n/a
n/a
18.8
19.28
n/a
n/a
Despite significant increases in renewable fuel use
in the United States, real-world constraints, such as
the slower than expected development of the cellulosic
biofuel industry and constraints in the marketplace
related to supply of certain biofuels to consumers, have
made the timeline laid out by Congress for the growth
a
All values are ethanol-equivalent on an energy content basis,
except for BBD which is biodiesel-equivalent.
b
The 2017 BBD volume requirement was established in the
2014–2016 final rule (80 FR 77420, December 14, 2015).
200a
in renewable fuel use (other than for BBD) impossible
to achieve. These challenges continue, and are largely
the same for 2017 as they were for 2016. However, a
careful review of the comments we received in response
to the May 31, 2016 Notice of Proposed Rulemaking
(NPRM) and other information that has become available since May has led us to conclude that volume
reductions for 2017 need not be as great as we had
proposed. In light of the lower reductions necessary, in
this final rule we rely exclusively on the cellulosic waiver
authority to provide reductions in both advanced biofuel and total renewable fuel volumes. That is, we have
determined that it is not necessary to provide an additional increment of volume reduction for total renewable fuels through use of the general waiver authority
based on a finding of inadequate domestic supply,
as we had done in the final rule establishing annual
standards for 2014–2016 (“Renewable Fuel Standard
Program: Standards for 2014, 2015, and 2016 and
Biomass-Based Diesel Volume for 2017,” (hereinafter
referred to as the “2014–2016 final rule”),3 and as we
also proposed to do in establishing standards for 2017.4
We believe that the RFS program can and will drive
renewable fuel use, and we have considered the ability
of the market to respond to the standards we set when
we assessed the amount of renewable fuel that can be
reasonably attained in 2017. Therefore, while this
final rule applies the tools Congress provided to make
adjustments to the statutory volume targets in recognition of the constraints that exist today, we believe the
standards we are setting in this action will drive growth
in renewable fuels, particularly advanced biofuels,
3
80 FR 77420, December 14, 2015.
4
81 FR 34778, May 31, 2016.
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which achieve substantial lifecycle GHG emissions. In
our view, while Congress recognized that supply challenges may exist as evidenced by the waiver provisions, it did not intend growth in the renewable fuels
market to be stopped by those challenges, including
those associated with the “E10 blendwall.”5 The fact
that Congress chose to mandate increasing and substantial amounts of renewable fuel clearly signals that
it intended the RFS program to create incentives
to increase renewable fuel supplies and overcome constraints in the market. The standards we are setting
in this action will provide those incentives.
The standards we are setting in this final rule are
part of a collection of actions, in both the government
and private sectors, to increase the use of renewable
fuels. In addition to ongoing efforts to evaluate new
pathways for RIN generation for advanced biofuels,
we have recently proposed regulatory provisions that
we believe will enhance the ability of the market to
increase not only the production of advanced and cellulosic biofuels, but also the use of higher-level ethanol
blends such as E15 and E85.6 DOE and USDA are
continuing to provide funds for the development of new
technologies and expansion of infrastructure for higher
ethanol blends, and the ethanol industry has also made
efforts to expand the use of higher ethanol blends
5
The “E10 blendwall” represents the volume of ethanol that
can be consumed domestically if all gasoline contains 10% ethanol
and there are no higher-level ethanol blends consumed such as
E15 or E85.
6
See the recently proposed Renewables Enhancement and
Growth Support (REGS) Rule (81 FR 80828, November 16, 2016).
More information about this proposed rule can be found at
https://www.epa.gov/renewable-fuel-standard-program/proposed
-renewables-enhancement-and-growth-support-regs-rule.
202a
through its Prime the Pump program. These actions
are expected to continue to help clear hurdles to support the ongoing growth in the use of renewable fuels
in future years.
A. Purpose of This Action
The national volume targets of renewable fuel that
are intended to be achieved under the RFS program
each year (absent an adjustment or waiver by EPA)
are specified in CAA section 211(o)(2). The statutory
volumes for 2017 are shown in Table I.A–1. The cellulosic biofuel and BBD categories are nested within the
advanced biofuel category, which is itself nested within the total renewable fuel category. This means, for
example, that each gallon of cellulosic biofuel or BBD
that is used to satisfy the individual volume requirements for those fuel types can also be used to satisfy
the requirements for advanced biofuel and total renewable fuel.
TABLE I.A–1—APPLICABLE 2017 VOLUMES
SPECIFIED IN THE CLEAN AIR ACT
[Billion Gallons]a
Cellulosic biofuel
Biomass-based diesel
Advanced biofuel
Renewable fuel
5.5
≥1.0
9.0
24.0
Under the RFS program, EPA is required to determine and publish annual percentage standards for
each compliance year. The percentage standards are
calculated to ensure use in transportation fuel of the
national “applicable volumes” of the four types of bioa
All values are ethanol-equivalent on an energy content basis,
except values for BBD which are given in actual gallons.
203a
fuel (cellulosic biofuel, BBD, advanced biofuel, and total
renewable fuel) that are set forth in the statute or
established by EPA in accordance with the Act’s requirements. The percentage standards are used by obligated
parties (generally, producers and importers of gasoline
and diesel fuel) to calculate their individual compliance obligations. Each of the four percentage standards is applied to the volume of non-renewable gasoline
and diesel that each obligated party produces or imports during the specified calendar year to determine
their individual volume obligations with respect to the
four renewable fuel types. The individual volume
obligations determine the number of RINs of each
renewable fuel type that each obligated party must
acquire and retire to demonstrate compliance.
EPA is establishing the annual applicable volume
requirements for cellulosic biofuel, advanced biofuel,
and total renewable fuel for 2017, and for BBD for
2018.7 Table I.A–2 lists the statutory provisions and
associated criteria relevant to determining the national
applicable volumes used to set the percentage standards in this final rule.
7
The 2017 BBD volume requirement was established in the
2014–2016 final rule.
204a
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TABLE I.A—2—STATUTORY PROVISIONS FOR DETERMINATION OF APPLICABLE VOLUMES
Applicable
Clean air act
Criteria provided in statute for
volumes
reference
determination of applicable volume
Cellulosic biofuel ........... 211(o)(7)(D)(i) ............ Required volume must be lesser of volume specified in CAA
211(o)(2)(B)(i)(III) or EPA’s projected volume.
211(o)(7)(A) ................ EPA in consultation with other federal agencies may waive the
statutory volume in whole or in part if implementation would
severely harm the economy or environment of a State, region, or
the United States, or if there is an inadequate domestic supply.
Biomass-based
211(o)(2)(B)(ii)
Required volume for years after 2012 must be at least 1.0 billion
8
diesel ............................ and (v) ........................ gallons, and must be based on a review of implementation of the
program, coordination with other federal agencies, and an analysis
of specified factors.
211(o)(7)(A) ................ EPA in consultation with other federal agencies may waive the statutory volume in whole or in part if implementation would severely
harm the economy or environment of a State, region, or the United
States, or if there is an inadequate domestic supply.
Advanced biofuel ........... 211(o)(7)(D)(i) ............ If applicable volume of cellulosic biofuel is reduced below the statutory volume to the projected volume, EPA may reduce the advanced
biofuel and total renewable fuel volumes in CAA 211(o)(2)(B)(i)(I)
and (II) by the same or lesser volume. No criteria specified.
211(o)(7)(A) ................ EPA in consultation with other federal agencies may waive the statutory volume in whole or in part if implementation would severely
harm the economy or environment of a State, region, or the United
States, or if there is an inadequate domestic supply.
Total renewable
211(o)(7)(D)(i) ............ If applicable volume of cellulosic biofuel is reduced below the statufuel .................................
tory volume to the projected volume, EPA may reduce the advanced
biofuel and total renewable fuel volumes in CAA 211(o)(2)(B)(i)(I)
and (II) by the same or lesser volume. No criteria specified.
211(o)(7)(A) ................ EPA in consultation with other federal agencies may waive the statutory volume in whole or in part if implementation would severely
harm the economy or environment of a State, region, or the United
States, or if there is an inadequate domestic supply.
8
Section 211(o)(7)(E) also authorizes EPA in consultation with other federal agencies to issue a temporary waiver of applicable volumes
of BBD where there is a significant feedstock disruption or other market circumstance that would make the price of BBD fuel increase
significantly.
205a
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207a
As shown in Table I.A–2, the statutory authorities
allowing EPA to modify or set the applicable volumes
differ for the four categories of renewable fuel. Under
the statute, EPA must annually determine the
projected volume of cellulosic biofuel production for
the following year. If the projected volume of cellulosic
biofuel production is less than the applicable volume
specified in section 211(o)(2)(B)(i)(III) of the statute,
EPA must lower the applicable volume used to set the
annual cellulosic biofuel percentage standard to the
projected production volume. In Section III of this final
rule, we present our analysis of cellulosic biofuel production and the final applicable volume for 2017. This
analysis is based on information provided by the
Department of Energy’s Energy Information Administration (EIA), an evaluation of producers’ production
plans and progress to date following discussions with
cellulosic biofuel producers, and is informed by comments we received in response to the NPRM.
With regard to BBD, Congress chose to set aside a
portion of the advanced biofuel standard for BBD, and
CAA section 211(o)(2)(B) specifies the applicable volumes of BBD to be used in the RFS program only
through year 2012. For subsequent years the statute
sets a minimum volume of 1 billion gallons, and directs
EPA, in coordination with the U.S. Departments of
Agriculture (USDA) and Energy (DOE), to determine
the required volume after review of implementation of
the renewable fuels program and consideration of a
number of factors. The BBD volume requirement must
be established 14 months before the year in which it
will apply. In the 2014–2016 final rule we established
the BBD volume for 2017. In Section VI of this preamble we discuss our assessment of statutory and other
relevant factors and our final volume requirement for
BBD for 2018, which has been developed in coordina-
208a
tion with USDA and DOE. We are increasing the
required volume of BBD so as to provide continued
support to that important contributor to the pool of
advanced biofuel while at the same time setting the
volume requirement in a manner anticipated to provide continued incentive for the development of other
types of advanced biofuel.
Regarding advanced biofuel and total renewable fuel,
Congress provided several mechanisms through which
those volumes could be reduced if necessary. If we
reduce the applicable volume of cellulosic biofuel below
the volume specified in CAA section 211(o)(2)(B)(i)(III),
we also have the authority to reduce the applicable
volumes of advanced biofuel and total renewable fuel
by the same or a lesser amount. We refer to this as the
“cellulosic waiver authority.” We may also reduce the
applicable volumes of any of the four renewable fuel
types using the “general waiver authority” provided in
CAA section 211(o)(7)(A) if EPA, in consultation with
USDA and DOE, finds that implementation of the
statutory volumes would severely harm the economy
or environment of a State, region, or the United States,
or if there is inadequate domestic supply. Sections II,
IV, and V of this final rule describe our use of the
cellulosic waiver authority alone to reduce volumes of
advanced biofuel and total renewable fuel, and our
assessment that the resulting volumes are reasonably
attainable. As described in the NPRM, and consistent
with the views that we expressed in the 2014–2016
final rule, we continue to believe that reductions in the
statutory targets for 2017 are necessary. However, in
light of our review of updated information and consideration of comments, we are making those reductions
under the cellulosic waiver authority alone and are not
finalizing an additional increment of reduction for total
renewable fuel based on a finding of inadequate domes-
209a
tic supply under the general waiver authority as we
had proposed. Despite the reductions we are finalizing
today, we continue to be mindful that the primary
objective of the statute is to increase renewable fuel
use over time. While progress has taken longer than
Congress anticipated, we note that today’s rule provides for 15 billion gallons of conventional renewable
fuel, the implied level envisioned under the statute for
2017, while also providing for a substantial increase in
the required volume of advanced biofuel over past
volume requirements.
B. Summary of Major Provisions in This Action
This section briefly summarizes the major provisions of this final rule. We are establishing applicable
volume requirements and associated percentage standards for cellulosic biofuel, advanced biofuel, and total
renewable fuel for 2017, as well as the percentage standard for BBD for 2017, and the applicable volume requirement for BBD for 2018.
1. Approach to Setting Volume Requirements
The approach we have taken in this final rule is
essentially the same as that presented in the NPRM
and in the 2014–2016 final rule with regard to establishing the cellulosic biofuel volume requirement, and
the use of the cellulosic waiver authority to reduce
advanced biofuel and total renewable fuel. However, it
differs in that we have not found it necessary to also
use the general waiver authority to provide an additional increment of reduction with respect to total
renewable fuel. While in the NPRM we proposed to
determine the maximum reasonably achievable supply of total renewable fuel, consistent with the general
waiver authority’s “inadequate domestic supply” crite-
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rion, in this final rule we have instead identified the
total renewable fuel volume that results from use of
the cellulosic waiver authority, and have determined
that this volume of total renewable fuel is reasonably
attainable. In this assessment, we took into account
the same constraints in the supply of renewable fuel
we noted in the NPRM, but have come to a different
result with respect to necessary volume reductions in
light of updated information and consideration of comments.
Section II provides a general description of our
approach to setting volume requirements in today’s
rule, including a review of the statutory waiver authorities and our consideration of carryover RINs. Section
III provides our assessment of the 2017 cellulosic
biofuel volume based on a projection of production that
reflects a neutral aim at accuracy. Sections IV and V
describe our assessment of reasonably attainable volumes of advanced biofuel and total renewable fuel,
respectively. Finally, Section VI provides our determination regarding the 2018 BBD volume requirement,
and reflects an analysis of a set of factors stipulated in
CAA section 211(o)(2)(B)(ii).
2. Cellulosic Biofuel
In the past several years the cellulosic biofuel industry has continued to make progress towards increased
commercial scale production. Cellulosic biofuel production reached record levels in 2015, driven largely
by compressed natural gas (CNG) and liquefied natural gas (LNG) derived from biogas, and is expected to
exceed these volumes in 2016. Cellulosic ethanol, while
produced in much smaller quantities than CNG/LNG
derived from biogas, was produced consistently on a
commercial scale for the first time in 2015. Cellulosic
ethanol production levels increased from existing facil-
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ities in 2016, and significant work continues to be done
to enable the production of cellulosic ethanol at new
facilities in 2017 and beyond. Available data suggest
that the production levels for both cellulosic CNG/LNG
and cellulosic ethanol in 2016 will exceed by a significant margin the levels produced in 2015. In this rule
we are establishing a cellulosic biofuel volume requirement of 311 million ethanol-equivalent gallons for 2017
based on the information we have received regarding
individual facilities’ capacities, production start dates
and biofuel production plans, information received in
public comments, input from other government agencies, and EPA’s own engineering judgment.
As part of estimating the volume of cellulosic biofuel
that will be made available in the U.S. in 2017, we considered all potential production sources by company
and facility. This included facilities still in the commissioning or start-up phases, as well as facilities
already producing some volume of cellulosic biofuel.9
From this universe of potential cellulosic biofuel sources,
we identified the subset that is expected to produce
commercial volumes of qualifying cellulosic biofuel for
use as transportation fuel, heating oil, or jet fuel by
the end of 2017. To arrive at projected volumes, we
collected relevant information on each facility. We
then developed projected production ranges based on
factors such as the status of the technology being used,
progress towards construction and production goals,
facility registration status, production volumes
achieved, and other significant factors that could poten9
Facilities primarily focused on research and development
(R&D) were not the focus of our assessment, as production from
these facilities represents very small volumes of cellulosic biofuel,
and these facilities typically have not generated RINs for the fuel
they have produced.
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tially impact fuel production or the ability of the
produced fuel to qualify for cellulosic biofuel Renewable Identification Numbers (RINs). We also used this
information to group these companies based on production history and to select a value within the aggregated
projected production ranges that we believe best represents the most likely production volume from each
group of companies in 2017. Further discussion of
these factors and the way they were used to determine
our final cellulosic biofuel projection for 2017 can be
found in Section III.
3. Advanced Biofuel
The conditions that compelled us to reduce the 2016
volume requirement for advanced biofuel below the
statutory target remain relevant in 2017. As for 2016,
we investigated the ability of volumes of non-cellulosic
advanced biofuels to backfill unavailable volumes of
cellulosic biofuel in 2017, through domestic production
or import. We took into account the substantial GHG
emissions reduction required of advanced biofuels, the
various constraints on supply of advanced biofuels, the
ability of the standards we set to bring about market
changes in the time available, and the potential impacts
associated with diverting some feedstocks from current use to the production of biofuel. Based on these
considerations and review of the comments received in
response to the NPRM and other information that has
become available, we have determined that a portion
of the shortfall in cellulosic biofuel may appropriately
be backfilled with advanced biofuel. We are exercising
our cellulosic waiver authority to reduce the statutory
applicable volume of advanced biofuel to a final volume requirement of 4.28 billion gallons for 2017. This
is somewhat higher than the proposed level of 4.0 billion gallons. The applicable volume for advanced bio-
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fuel that we are establishing for 2017 will result in
significant volume growth over the volume requirement for 2016, and will require the use of more noncellulosic advanced biofuel (3.97 billion gallons) than
would have been required under the statutory targets
(3.50 billion gallons).
4. Total Renewable Fuel
Following our determination of the appropriate
volume reduction for advanced biofuel for 2017 using
the cellulosic waiver authority, we applied the same
volume reduction to the statutory target for total renewable fuel, resulting in a volume requirement of 19.28
billion gallons. We then evaluated this total renewable
fuel volume to determine if it is reasonably attainable
given assessments of attainable volumes of individual
fuel types, including biodiesel, renewable diesel, ethanol (in the form of E10 or higher ethanol blends such
as E15 or E85, taking into account demand for E0),
and other renewable fuels. Based on comments received
in response to the NPRM and other information that
has become available, we have determined that a total
renewable fuel volume of 19.28 billion gallons is reasonably attainable in 2017. There is, therefore, no need
to use the general waiver authority to further reduce
the total renewable fuel volume requirement due to a
finding of inadequate domestic supply.10
10
The general waiver authority can also be used under a determination that the RFS volumes would cause “severe economic or
environmental harm.” As described in Section II.A.2 and in more
detail in the response to comments document accompanying this
rule, EPA does not believe that the record supports a finding of
severe economic or environmental harm with respect to the volume requirements we are finalizing today.
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5. Biomass-Based Diesel
In EISA, Congress specified increasing applicable
volumes of BBD through 2012. Beyond 2012 Congress
stipulated that EPA, in coordination with other agencies, was to establish the BBD volume taking into consideration implementation of the program to date and
various specified factors, providing that the required
volume for BBD could not be less than 1.0 billion gallons. For 2013, EPA established an applicable volume
of 1.28 billion gallons. For 2014 and 2015 we established the BBD volume requirement to reflect the
actual volume for each of these years of 1.63 and 1.73
billion gallons.11 For 2016 and 2017, we set the BBD
volume requirements at 1.9 and 2.0 billion gallons
respectively.
Given current and recent market conditions, the
advanced biofuel volume requirement is driving the
use of biodiesel and renewable diesel volumes over and
above volumes required through the separate BBD
standard, and we expect this to continue. Nevertheless,
we continue to believe for 2018 that it is appropriate
to set increasing BBD applicable volumes to provide a
floor to support continued investment to enable
increased production and use of BBD. In doing so we
also believe in the importance of maintaining opportunities within the advanced biofuel requirement for
growth in other types of advanced biofuel, such as
renewable diesel co-processed with petroleum, renewable gasoline blend stocks, and renewable heating oil,
as well as others that are under development.
11
The 2015 BBD standard was based on actual data for the
first 9 months of 2015 and on projections for the latter part of the
year for which data on actual use was not available at the time.
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Thus, based on a review of the implementation of
the program to date and all the factors required under
the statute, and in coordination with USDA and DOE,
we are finalizing an increase in the applicable volume
of BBD by 100 million gallons, to 2.1 billion gallons for
2018. We believe that this increase will support the
overall goals of the program while also maintaining
the incentive for development and growth in production of other advanced biofuels. Establishing the volumes at this level will encourage BBD producers to
manufacture higher volumes of fuel that will contribute to the advanced biofuel and total renewable fuel
requirements, while also leaving considerable opportunity within the advanced biofuel mandate for investment in and growth in production of other types of
advanced biofuel with comparable or potentially superior environmental or other attributes.
6. Annual Percentage Standards
The renewable fuel standards are expressed as a
volume percentage and are used by each producer and
importer of fossil-based gasoline or diesel to determine
their renewable fuel volume obligations. The percentage standards are set so that if each obligated party
meets the standards, and if EIA projections of gasoline
and diesel use for the coming year prove to be accurate,
then the amount of renewable fuel, cellulosic biofuel,
BBD, and advanced biofuel actually used will meet the
volume requirements used to derive the percentage
standards, required on a nationwide basis.
Four separate percentage standards are required
under the RFS program, corresponding to the four separate renewable fuel categories shown in Table I.A–1.
The specific formulas we use in calculating the renewable fuel percentage standards are contained in the
regulations at 40 CFR 80.1405. The percentage stand-
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ards represent the ratio of renewable fuel volume to
projected non-renewable gasoline and diesel volume.
The volume of transportation gasoline and diesel used
to calculate the final percentage standards was provided by the Energy Information Administration (EIA).
The final percentage standards for 2017 are shown in
Table I.B.6–1. Detailed calculations can be found in
Section VII, including the projected gasoline and
diesel volumes used.
TABLE I.B.6–1—FINAL 2017
PERCENTAGE STANDARDS
Cellulosic biofuel ........................
Biomass-based diesel .................
Advanced biofuel ........................
Renewable fuel ...........................
0.173%
1.67%
2.38%
10.70%
7. Assessment of Aggregate Compliance
By November 30 of each year we are required to
assess the status of the aggregate compliance approach
to land-use restrictions under the definition of renewable biomass for both the U.S. and Canada. In today’s
action we are providing the final announcements for
these administrative actions.
As part of the RFS regulations, EPA established an
aggregate compliance approach for renewable fuel producers who use planted crops and crop residue from
U.S. agricultural land. This compliance approach
relieved such producers (and importers of such fuel) of
the individual recordkeeping and reporting requirements otherwise required of producers and importers
to verify that such feedstocks used in the production of
renewable fuel meet the definition of renewable
biomass. EPA determined that 402 million acres of
U.S. agricultural land was available in 2007 (the year
of EISA enactment) for production of crops and crop
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residue that would meet the definition of renewable
biomass, and determined that as long as this total
number of acres is not exceeded, it is unlikely that new
land has been devoted to crop production based on historical trends and economic considerations. We indicated that we would conduct an annual evaluation of
total U.S. acreage that is cropland, pastureland, or
conservation reserve program land, and that if the
value exceeds 402 million acres, producers using domestically grown crops or crop residue to produce renewable fuel would be subject to individual recordkeeping
and reporting to verify that their feedstocks meet the
definition of renewable biomass. As described in Section VIII.A, based on data provided by the USDA and
using the methodology in place since 2014, we have
estimated that U.S. agricultural land totaled approximately 380 million acres in 2016 and thus did not exceed
the 2007 baseline acreage. This assessment means that
the aggregate compliance provision can continue to be
used in the U.S. for calendar year 2017.
On September 29, 2011, EPA approved the use of a
similar aggregate compliance approach for planted
crops and crop residue grown in Canada. The Government of Canada utilized several types of land use data
to demonstrate that the land included in their 124 million acre baseline is cropland, pastureland or land equivalent to U.S. Conservation Reserve Program land that
was cleared or cultivated prior to December 19, 2007,
and was actively managed or fallow and non-forested
on that date (and is therefore RFS2 qualifying land).
As described in Section VIII.B, based on data provided
by Canada, we have estimated that Canadian agricultural land totaled approximately 118.4 million acres in
2016 and thus did not exceed the 2007 baseline acreage. This assessment means that the aggregate com-
218a
pliance provision can continue to be used in Canada
for calendar year 2017.
II. Authority and Need For Waiver of Statutory Applicable Volumes
The statute provides the EPA with the authority to
reduce volume requirements below the applicable volume targets specified in the statute under specific circumstances. This section discusses those authorities and
our use of the cellulosic waiver authority alone to set
2017 volume requirements for cellulosic biofuel,
advanced biofuel, and total renewable fuel that are
below the statutory volume targets.
A. Statutory Authorities for Reducing Volume
Targets
In CAA section 211(o)(2), Congress specified increasing annual volume targets for total renewable fuel,
advanced biofuel, and cellulosic biofuel for each year
through 2022, and for biomass-based diesel through
2012, and authorized EPA to set volume requirements
for subsequent years in coordination with USDA and
DOE, and after consideration of specified factors. However, Congress also recognized that under certain circumstances it would be appropriate for EPA to set
volume requirements at a lower level than reflected in
the statutory volume targets, and thus provided waiver
provisions in CAA section 211(o)(7).
1. Cellulosic Waiver Authority
Section 211(o)(7)(D)(i) of the CAA provides that if
EPA determines that the projected volume of cellulosic
biofuel production for a given year is less than the
applicable volume specified in the statute, that EPA
must reduce the applicable volume of cellulosic biofuel
required to the projected production volume for that
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calendar year. In making this projection, EPA must
take a “neutral aim at accuracy.” API v. EPA, 706 F.3d
474 (D.C. Cir. 2013). Pursuant to this provision, EPA
has set the cellulosic biofuel requirement lower than
the statutory volumes for each year since 2010. As
described in Section III.D, the projected volume of
cellulosic biofuel production for 2017 is less than the
5.5 billion gallon volume target in the statute. Therefore, for 2017, we are setting the cellulosic biofuel volume requirement at a level lower than the statutory
applicable volume, in accordance with this provision.
Section 211(o)(7)(D)(i) also provides that “[f]or any
calendar year in which the Administrator makes . . . a
reduction [in cellulosic biofuel volumes], the Administrator may also reduce the applicable volume of
renewable fuel and advanced biofuels . . . by the same
or a lesser volume.” Using this authority, the reductions in total renewable fuel and advanced biofuel can
be less than or equal to, but no more than, the amount
of reduction in the cellulosic biofuel volume. EPA used
this authority to reduce applicable volumes of advanced
biofuel in 2014–16, and to reduce the total renewable
fuel volumes in those years by an equal amount. We
refer to authority in Section 211(o)(7)(D)(i) to waive
volumes of advanced and total renewable fuel as the
“cellulosic waiver authority.”
The cellulosic waiver authority was discussed by the
United States Court of Appeals for the District of
Columbia Circuit, in the context of its consideration of
a judicial challenge to the rule establishing the 2013
annual RFS standards. As the court explained,
The Clean Air Act provides that if EPA
reduces the cellulosic biofuel requirement, as
it did here, then it ‘may also reduce’ the advanced biofuel and total renewable fuel quotas
220a
‘by the same or a lesser volume.’ 42 U.S.C.
7545(o)(7)(D)(i). There is no requirement to
reduce these latter quotas, nor does the statute prescribe any factors that EPA must consider in making its decision. See id. In the
absence of any express or implied statutory
directive to consider particular factors, EPA
reasonably concluded that it enjoys broad
discretion regarding whether and in what
circumstances to reduce the advanced biofuel
and total renewable fuel volumes under the
cellulosic waiver provision. Monroe v. EPA,
750 F.3d 909, 915 (D.C. Cir. 2014).
Some stakeholders have commented that EPA may
only exercise the cellulosic waiver authority to reduce
total and advanced volumes in circumstances described
in CAA section 211(o)(7)(A) (that is, where there is
inadequate domestic supply or severe harm to the
environment or economy), or that it must in using the
cellulosic waiver authority consider the factors specified in section 211(o)(2)(B)(ii) that are required considerations when EPA sets applicable volumes for years
in which the statute does not do so. Contrary to these
comments, the Court found in the Monroe case that the
statute does not prescribe any factors that EPA must
consider in making is decision; EPA has broad discretion under 211(o)(7)(D)(i) to determine when and under
what circumstances to reduce the advanced and total
renewable fuel volumes when it reduces the statutory
applicable volume of cellulosic biofuel.
When using the cellulosic waiver authority, we believe
that there would be substantial justification to exercise our discretion to lower volumes of total and
advanced biofuels in circumstances where there are
questions regarding the sufficiency of production or
221a
import of potentially qualifying renewable fuels, and
where there is evidence of constraints that would limit
the ability of those biofuels to be used for purposes
specified in the Act (i.e., in transportation fuel, heating
oil, or jet fuel). In addition, we believe that it is appropriate in exercising the cellulosic waiver authority for
EPA to consider the Congressional objectives reflected
in the volumes tables in the statute, and the environmental objectives that generally favor the use of
advanced biofuels over non-advanced biofuels. For
example, in light of the larger GHG emissions reductions required for advanced biofuels as compared to
conventional biofuel, and the Congressional objective
to dramatically increase their use in the time period
between 2015 and 2022, we believe that it is generally
appropriate for reasonably attainable volumes of
advanced biofuel that are sourced in a manner expected
to provide significant GHG reduction benefits to backfill for shortages in cellulosic biofuel. On the other
hand, we do not believe it would be appropriate for the
gap in the availability of cellulosic biofuel in 2017 to
be filled or partially filled with non-advanced biofuel,
taking into consideration both the substantially lower
greenhouse gas emissions reductions required for nonadvanced biofuel12 and the Congressional intent
reflected in the statutory tables that use of these
biofuels in this time period would be limited.13 These
12
Non-advanced biofuel must meet the 20% reduction in
lifecycle GHG emissions described in CAA section 211(o)(2)(A)(i),
unless they qualify for an exemption under 40 CFR 80.1403.
13
Since the advanced biofuel volume requirement is nested
within the total renewable fuel volume requirement, the statutory implied volume for conventional renewable fuel in the statutory tables can be discerned by subtracting the applicable volume
of advanced biofuel from that of total renewable fuel. Performing
this calculation with respect to the tables in CAA section
222a
considerations are consistent with EPA’s past interpretation of the cellulosic waiver authority as envisioning equivalent reductions in the applicable volumes of advanced biofuels and total renewable fuels.14
See 74 FR 24914; 78 FR 49810.
We believe, as we did in setting the volumes in the
past, that the circumstances justifying use of our cellulosic waiver authority and thus a reduction in statutory
volumes are currently present, and we are again using
our cellulosic waiver authority under 211(o)(7)(D)(i) to
reduce volume requirements for advanced biofuel and
total renewable fuel. Congress envisioned that there
would be 5.5 billion gallons of cellulosic biofuel in 2017,
while our production projection, described in detail
in Section III, is for 311 million gallons. Under
211(o)(7)(D)(i), EPA must lower the required cellulosic
volume to the projected production volumes. See also
API v. EPA, 706 F.3d 474 (D.C. Cir. 2012). Doing so
also provides EPA with authority to lower advanced
and total renewable fuel volumes by the same or a
lesser amount.
211(o)(2)(B) indicates a Congressional expectation that in the
time period 2015–2022, advanced biofuel volumes would grow
from 5.5 to 21 billion gallons, while the implied volume for
conventional renewable fuel would remain constant at 15 billion
gallons.
14
Our consistent view has been that the provision is best interpreted and implemented to provide for equal reductions in advanced
biofuel and total renewable fuel. We believe that this approach is
consistent with the statutory language and best effectuates the
objectives of the statute, in that it allows for EPA to determine
an appropriate volume of advanced biofuel providing meaningful
GHG emissions reductions to backfill missing cellulosic volumes,
while also resulting in an implied volume for conventional
renewable fuel of no greater than 15 billion gallons as envisioned
in the statutory time period for 2015–2022.
223a
We have determined, as described in Section IV, that
the applicable volume for advanced biofuels specified
in the statute for 2017 cannot be achieved and, consistent with the principles described above, we are
exercising our cellulosic waiver authority to lower the
applicable volume of advanced biofuel to a level that is
both reasonably attainable and appropriate, and to
provide an equivalent reduction in the applicable volume of total renewable fuel. In addition, we have
determined that there is adequate supply to satisfy the
total renewable fuel volume derived through applying
an equal volume reduction as for advanced biofuel.
Therefore, no further reductions of the total renewable
fuel volume requirement are necessary to address concerns of inadequate supply. The resulting volume
requirements provide the benefits associated with the
use of reasonably attainable and appropriate volumes
of advanced biofuels to partially backfill for missing
volumes of cellulosic biofuel in 2017, while also providing for an implied volume requirement for conventional biofuel equal to that envisioned by Congress for
2017.
2. General Waiver Authority
Section 211(o)(7)(A) of the CAA provides that EPA,
in consultation with the Secretary of Agriculture and
the Secretary of Energy, may waive the applicable volume specified in the Act in whole or in part based on
petition by one or more States, by any person subject
to the requirements of the Act, or by the EPA Administrator on her own motion. Such a waiver must be
based on a determination by the Administrator, after
public notice and opportunity for comment that (1)
implementation of the requirement would severely
harm the economy or the environment of a State, a
region or the United States, or (2) there is an inade-
224a
quate domestic supply. Because the general waiver
provision provides EPA the discretion to waive the
statutory applicable volume “in whole or in part,” we
interpret this section as granting EPA authority to
fully or partially waive any of the four applicable volume requirements in appropriate circumstances. For
the years 2014–2016, EPA determined that there was
an inadequate domestic supply of total renewable fuel,
and used the general waiver authority to reduce the
total renewable fuel volumes further than the reductions obtained using the cellulosic waiver authority. In
the notice of proposed rulemaking for this rule, EPA
proposed to use the general wavier authority in a similar way, and for the same reason, in establishing the
2017 total renewable fuel volume requirement.
Based on further evaluation of the availability of
renewable fuel in the market, in the interim between
the NPRM and this final rule, and review of public
comment, EPA has determined that it is not necessary
to use the general waiver authority. That is, we have
determined that use of the cellulosic waiver authority
alone will be sufficient to yield a volume requirement
that is consistent with available supply.15
15
Some commenters noted that in addition to the authority to
reduce applicable volumes under the general waiver authority on
the basis of an “inadequate domestic supply” that EPA possesses
the ability to use the general waiver authority where it finds that
the RFS volumes would cause “severe economic or environmental
harm in a State, region, or the United States.” As described in
more detail in the response to comments document accompanying
this rule, EPA does not believe that the record supports a finding
of severe economic or environmental harm with respect to the
volume requirements we are finalizing today.
225a
3. General Comments Related to Waiver
Authorities
Many commenters suggested that EPA should only
use the cellulosic waiver authority to reduce volumes
of total renewable fuel in 2017. While we do not believe
this would have been possible under the circumstances
described in the proposal, in light of EPA’s re-evaluation
of available supplies, as discussed in Sections IV and
V, we are today following the approach suggested by
these commenters in using the cellulosic waiver authority exclusively to reduce volumes of both advanced
biofuel and total renewable fuel.
Some commenters said that EPA should not reduce
the volume requirements for advanced biofuel and total
renewable fuel at all and should instead set standards
for 2017 based on the statutory targets. In most cases,
these commenters based their positions on the availability of carryover RINs and an expectation that “letting the market work” would be sufficient to overcome
all constraints related the production and distribution
of fuels that can be used to satisfy these standards. As
described in Section II.B below, we continue to believe
that, in light of the expected volume of carryover RINs,
it would be inappropriate for 2017 to intentionally
draw down the bank of carryover RINs for the purposes
of increasing the volume requirements above levels
that can be satisfied with physical volume. As for “letting the market work,” we believe that this view is dismissive of the market constraints discussed in the
NPRM, Table II.E. 1–1 of the 2014–2016 final rule and
in Sections IV.B and V.B of this final rule. The market
is not unlimited in its ability to respond to the standards EPA sets. While setting the standards at the
statutory targets would undoubtedly produce a significant increase in RIN prices, doing so in light of the
226a
combined actions of all constraints shown in Table
II.E.1–1 of the 2014–2016 final rule and discussed in
Sections IV.B. and V.B. of this rule would nevertheless
create a shortfall in supply in 2017 that would likely
lead to a complete draw-down in the bank of carryover
RINs, noncompliance, and/or additional petitions for a
waiver of the standards. As described in Sections IV
and V, we are authorized to use the cellulosic waiver
authority in 2017 to reduce volumes of advanced and
total renewable fuel, and believe it is appropriate to do
so for the reasons noted in those sections.
B. Treatment of Carryover RINs
Consistent with our approach in the 2014–2016 final
rule, we have also considered the availability and role
of carryover RINs in our decision to exercise our cellulosic waiver authority in setting the advanced and
total volume requirements for 2017.16 Although the statute requires a credit program and specifies that the
credits shall be valid for a 12-month time period, neither the statute nor EPA regulations specify how or
whether EPA should consider the availability of carryover RINs in exercising its cellulosic waiver authority.17
16
The discussion of the role of carryover RINs as they relate
to the cellulosic volume standard for 2017 can be found in Section
III.D.
17
CAA section 211(o)(5) requires that EPA establish a credit
program as part of its RFS regulations, and that the credits be
valid to show compliance for 12 months as of the date of generation. EPA implemented this requirement though the use of RINs,
which can be used to demonstrate compliance for the year in
which they are generated or the subsequent compliance year.
Obligated parties can obtain more RINs than they need in a given
compliance year, allowing them to “carry over” these excess RINs
for use in the subsequent compliance year, although use of these
carryover RINs is limited to 20% of the obligated party’s RVO.
For the bank of carryover RINs to be preserved from one year to
227a
As noted in the context of the rule establishing the
2014–16 RFS standards, we believe that a bank of
carryover RINs is extremely important in providing
obligated parties compliance flexibility in the face of
substantial uncertainties in the transportation fuel
marketplace, and in providing a liquid and well-functioning RIN market upon which success of the entire
program depends.18 Carryover RINs provide flexibility
in the face of a variety of circumstances that could limit
the availability of RINs, including weather-related damage to renewable fuel feedstocks and other circumstances potentially affecting the production and distribution of renewable fuel.19 On the other hand, carryover RINs can be used for compliance purposes, and in
the context of the 2013 RFS rulemaking we noted that
an abundance of carryover RINs available in that year,
together with possible increases in renewable fuel production and import, justified maintaining the advanced
and total renewable fuel volume requirements for that
year at the levels specified in the statute.20
In the 2017 NPRM, EPA estimated that the likely
volume of the carryover RIN bank for 2017 would be
approximately 1.72 billion carryover RINs (including
all D codes). We proposed that in light of this relatively
the next, individual carryover RINs are used for compliance
before they expire and are essentially replaced with a newer
vintage RIN that is then held for use in the next year. For
example, if the volume of the RIN bank is unchanged from 2016
to 2017, then all of the vintage 2016 carryover RINs must be used
for compliance in 2017, or they will expire. However, the same
volume of 2017 RINs can then be “banked” for use in the next
year.
18
See 80 FR 77482–77487 (December 14, 2015).
19
See id., and 72 FR 23900 (May 1, 2007).
20
See 79 FR 49794 (August 15, 2013).
228a
limited volume and the important functions provided
by the RIN bank, that we would not set the volume
requirements for 2017 in a manner that would intentionally lead to a drawdown in the bank of carryover
RINs. In their comments on the 2017 NPRM, parties
generally expressed two opposing points of view. Commenters representing obligated parties supported EPA’s
proposed decision to not assume a drawdown in the
bank of carryover RINs in determining the appropriate level of volume requirements. These commenters
reiterated the importance of maintaining the carryover RIN bank in order to provide obligated parties
with necessary compliance flexibilities, better market
trading liquidity, and a cushion against future program uncertainty. Commenters representing renewable fuel producers, however, contended that carryover
RINs represent actual supply and should be accounted
for when establishing the annual volume standards
and, in particular, in any determination under the
general waiver authority that there is an “inadequate
domestic supply.” They expressed concern that obligated parties could use carryover RINs as an alternative to RINs generated for renewable fuel produced in
2017, leading to less demand for their product and
inadequate return on investment.21
1. Updated Projection of Carryover RIN
Volume
In the NPRM, EPA estimated that the carryover
RIN bank available in 2017 would be approximately
1.72 billion carryover RINs. Since that time, obligated
parties have submitted their compliance demonstra21
A full description of comments received, and our detailed
responses to them, is available in the Response to Comments document in the docket.
229a
tions for the 2014 compliance year and, based on that
information, we now estimate that there will at most
be 1.54 billion carryover RINs available for possible use
in complying with the standards for 2017, a decrease of
nearly 200 million RINs from the previous estimate.22
This is approximately 8 percent of the final 2017 total
renewable fuel volume standard and less than half of
the 20 percent limit permitted by the regulations to be
carried over for use in complying with the 2017 standards. However, there remains considerable uncertainty
surrounding this number since compliance demonstrations still need to be made for the 2015 and 2016 RFS
standards, and it is unclear at this time whether some
portion of the 1.54 billion carryover RINs we estimate
will be available for the 2017 compliance demonstrations will be used for compliance prior to 2017. In
addition, we note that there have been enforcement
actions in past years that have resulted in the retirement of RINs that were fraudulently generated and
were therefore invalid, and parties that relied on those
invalid RINs for compliance were required to acquire
valid substitutes to true up their past compliance
demonstrations. Future enforcement actions could
have similar results, and require that obligated parties
settle past enforcement-related obligations in addition
to the annual standards, thereby potentially creating
demand for RINs greater than can be accommodated
through actual renewable fuel blending in 2017.
Collectively, the result of satisfying RFS obligations
in 2015 and 2016 and settling enforcement-related
accounts could be an effective reduction in the size of
the collective bank of carryover RINs to a level below
22
The calculations performed to estimate the number of carryover RINs available in 2017 can be found in the memorandum,
“2017 Carryover RIN Bank Calculations,” available in the docket.
230a
1.54 billion RINs. Thus, we believe there is considerable uncertainty that a RIN bank as large as 1.54 billion
RINs will be available in 2017.
2. EPA’s Decision
EPA has decided to maintain the proposed approach,
and not set the volume requirements in the final rule
with the intention or expectation of drawing down the
current bank of carryover RINs. In finalizing this
approach, we carefully considered the many comments
received, including on the role of carryover RINs under
our waiver authorities and the policy implications of
our decision. While we have not assumed an intentional drawdown in the overall bank of carryover RINs
owned by obligated parties collectively in establishing
the volume requirements for 2017, we understand that
some obligated parties may choose to sell or use all or
part of their individual banks of carryover RINs. To
the extent that they do so, other obligated parties
would be in a position to bank carryover RINs by using
available renewable fuel or purchasing RINs representing such fuel, with the expected net result being
no effective change in the size of the overall bank of
carryover RINs that is owned collectively by obligated
parties.
In response to those parties who argued that carryover RINs must be considered part of the “supply” when
EPA uses the general waiver authority on the basis of
a finding of “inadequate domestic supply,” we note that
we are not using the general waiver authority in this
final action, so these arguments are irrelevant. We
believe that a balanced consideration of the possible
role of carryover RINs in achieving the statutory volume objectives for advanced and total renewable fuels,
versus maintaining an adequate bank of carryover
RINs for important programmatic functions, is appro-
231a
priate when EPA exercises its discretion under the
cellulosic waiver authority, and that the statute does
not specify the extent to which EPA should require a
drawdown in the bank of carryover RINs when it exercises this authority.
An adequate RIN bank serves to make the RIN market liquid and to avoid the possible need for adjustments to the standards. Just as the economy as a whole
functions best when individuals and businesses prudently plan for unforeseen events by maintaining inventories and reserve money accounts, we believe that the
RFS program functions best when sufficient carryover
RINs are held in reserve for potential use by the RIN
holders themselves, or for possible sale to others that
may not have established their own carryover RIN
reserves. Were there to be no RINs in reserve, then
even minor disruptions causing shortfalls in renewable
fuel production or distribution, or higher than expected
transportation fuel demand (requiring greater volumes
of renewable fuel to comply with the percentage standards that apply to all volumes of transportation fuel,
including the unexpected volumes) could lead to the
need for a new waiver of the standards, undermining
the market certainty so critical to the long term success of the RFS program. Furthermore, many obligated
parties lack the ability to separate one or more types
of RINs through blending. With a functioning liquid
RIN market this is not a problem because we expect
that these obligated parties will be able to comply by
securing these RINs on the open market. However, a
significant drawdown of the carryover RIN bank leading to a scarcity of RINs may stop the market from
functioning in an efficient manner, even where the
market overall could satisfy the standards. For all of
these reasons, the collective carryover RIN bank provides a needed programmatic buffer that both facili-
232a
tates individual compliance and provides for smooth
overall functioning of the program.23 With volume
requirements increasing annually, and the size of the
carryover RIN bank shrinking through use of carryover RINs in both 2013 and 2014, we believe it is
prudent not to intentionally draw down the RIN bank
for 2017 that we have determined will not likely be
larger than 1.54 billion carryover RINs, and which
could in fact be smaller.
For the reasons noted above, and consistent with the
approach we took in the 2014–2016 final rule, we have
determined that under current circumstances, an intentional drawdown of the carryover RIN bank should not
be assumed in establishing the 2017 volume requirements. The current bank of carryover RINs will provide
an important and necessary programmatic buffer that
will both facilitate individual compliance and provide
for smooth overall functioning of the program. Therefore, we are not setting renewable fuel volume requirements at levels that would envision the drawdown in
the bank of carryover RINs. However, we note that we
may or may not take a similar approach in future years;
we will assess the situation on a case-by-case basis
going forward, and take into account the size of the
carryover RIN bank in the future and any lessons
learned from implementing past rules.
[Content Omitted]
V. Total Renewable Fuel Volume for 2017
The national volume targets of total renewable fuel
to be used under the RFS program each year through
23
Here we use the term “buffer” as shorthand reference to all
of the benefits that are provided by a sufficient bank of carryover
RINs.
233a
2022 are specified in CAA section 211(o)(2)(B)(i)(I).
For 2017 the statute stipulates that the volume of total
renewable fuel should be 24 billion gallons. Since we
have determined that the statutory volume target for
cellulosic biofuel must be reduced to reflect the projected production volume of that fuel type in 2017, we
are authorized under CAA section 211(o)(7)(D)(i) to
reduce the advanced biofuel and total renewable fuel
targets by the same or a lesser amount. We also have
the authority to reduce any volume target under the
general waiver authority under specific conditions as
described in Section II.A.2. Although in the NPRM we
had proposed to use a combination of the cellulosic
waiver authority and the general waiver authority to
reduce the statutory volume target for total renewable
fuel for 2017, we have determined, based on comments
received in response to the NPRM and a review of
updated information, that 2017 supply is adequate to
meet a total renewable fuel volume requirement of
19.28 billion gallons resulting from the use of the
cellulosic waiver authority alone. The use of the
general waiver authority for 2017 to further reduce
the total renewable fuel standard is therefore not necessary. As a result, the implied volume for conventional (non-advanced) renewable fuel will be 15.0
billion gallons.
Today’s standards are significantly higher than
have been achieved in the past and will drive significant growth in renewable fuel use beyond what would
occur in the absence of the requirements. The final volume requirements for both advanced biofuel and total
renewable fuel recognize the ability of the market to
respond to the standards we set, thereby accomplishing the goals of the statute to increase renewable fuel
use.
234a
We investigated whether the market is on track to
meet the 2016 total renewable fuel volume requirement of 18.11 billion gallons, which EPA projected to
be the maximum achievable volume for that year in
the context of our use of the general waiver authority.
As described in a memorandum to the docket, supply
through the end of September coupled with a projection based on consideration of seasonal variations in
supply for previous years indicate that compliance
with the 2016 standards is indeed within reach.100 We
believe these results support the assessment conducted
for purposes of establishing the 2016 total renewable
fuel standard. For this final rule, we have taken a similar approach to assessing the adequacy of supply of
total renewable fuel that differs in some particulars as
described below.
A. Volumetric Limitation on Use of the Cellulosic
Waiver Authority
In Section IV.B we explained our use of the cellulosic
waiver authority to reduce the statutory volume target
for advanced biofuel to a level that we have determined is reasonably attainable and appropriate given
a consideration of factors related to the likely constraints on imports, distribution and use, and global
GHG impacts of incremental growth in advanced biodiesel and renewable diesel. This did not require a
reduction as large as the reduction in the statutory
volume target for cellulosic biofuel, and so this reduction was within the authority provided by CAA section
211(o)(7)(D)(i).
100
“Comparison of 2016 availability of RINs and 2016 standards,” memorandum from David Korotney to docket EPA–HQ–
OAR–2016–0004.
235a
As discussed in Section II.A.1, we believe that the
cellulosic waiver provision is best interpreted to require
equal reductions in advanced biofuel and total renewable fuel. We have consistently articulated this interpretation.101 Having determined that we should establish the advanced biofuel volume at a level requiring a
reduction of 4,719 million gallons from the statutory
target, applying an equal reduction to the statutory
target for total renewable fuel yields the results shown
below.
TABLE V.A–1—APPLYING EQUAL VOLUME
REDUCTIONS TO TOTAL RENEWABLE FUEL
AS FOR ADVANCED BIOFUEL UNDER
CELLULOSIC WAIVER AUTHORITY
[Million gallons]
Statutory target ...................
Reduction under the cellulosic waiver authority ............
Resulting volume .................
Advanced
Total
biofuel renewable
fuel
9,000 24,000
4,719
4,719
4,281
19,281
If we were to determine that there is an inadequate
domestic supply to satisfy the total renewable fuel volume resulting from use of the cellulosic waiver authority alone, we could use the general waiver authority,
described in Section II.A.2, to provide further reductions. Indeed, we proposed such an approach. However,
we have re-evaluated the situation in light of new data
and consideration of comments, and as described below
we have determined that there will be adequate supply
101
For instance, see discussion in the final rule setting the
2013 standards: 78 FR 49809–49810, August 15, 2013.
236a
to meet a total renewable fuel volume requirement of
19.28 billion gallons in 2017.102 As a result of this assessment, we have determined that further reductions in
the total renewable fuel applicable volume using the
general wavier authority are not necessary.
B. Assessing Adequacy of Supply
As noted above, the applicable volume of total renewable fuel was derived by applying the same volume
reduction to the statutory volume target for total
renewable fuel as was determined to be appropriate for
advanced biofuel, using the cellulosic waiver authority. This section describes our assessment that there is
adequate supply to meet an applicable volume requirement of 19.28 billion gallons. The objective of our
assessment is different than our analysis in the
NPRM, where we sought to identify the maximum
reasonably achievable volume of total renewable fuel
based on the sum of estimates of each type of renewable fuel, such as total ethanol, biodiesel and renewable
diesel, biogas, and other non-ethanol renewable fuels.
In this final rule, in contrast, we instead are evaluating those sources to determine if in the aggregate it
appears that there is adequate supply to meet the total
renewable fuel volume shown in Table V.A–1. Based
on our conclusion that there is sufficient supply as discussed below, it is unnecessary to address any inadequate domestic supply through use of the general
waiver authority.
Despite the different objective, we face much the
same challenges that we noted in the NPRM: It is a
102
Stakeholder comments most directly impacting our assessment of the adequacy of supply of total renewable fuel were directed
at distribution issues associated with biodiesel and renewable
diesel. See Section V.B.2 for further discussion.
237a
very challenging task to estimate the adequacy of supply
in light of the myriad complexities of the fuels market
and how individual aspects of the industry might change
in the future, and also because we cannot precisely
predict how the market will respond to the volumedriving provisions of the RFS program. This is the type
of assessment that is not given to precise measurement and necessarily involves considerable exercise of
judgment.
Our investigation into whether there is adequate
supply to meet the total renewable fuel volume shown
in Table V.A–1 was driven primarily by a consideration of the total amount of ethanol that can be reasonably attained in light of various constraints, and the
total volume of biodiesel and renewable diesel that can
be reasonably attained. We also considered smaller
contributions from non-ethanol cellulosic and other
non-ethanol renewable fuels (i.e. naphtha, heating oil,
butanol, and jet fuel). With regard to the more dominant contributors, the information that is available has
allowed us to make a relatively more precise estimate
of total supply of ethanol than of biodiesel/renewable
diesel. This is due to the fact that the primary constraints in the supply of ethanol in 2017 are readily
identifiable, although still challenging to quantify, while
there are many different factors that could potentially
constrain the supply of biodiesel and renewable diesel
in 2017. As a result, we did not attempt to derive a
specific estimate of reasonably attainable supply of
total biodiesel and renewable diesel. Instead, after
estimating what we consider to be reasonably attainable supply of ethanol in 2017, and taking into account
the estimates of non-ethanol cellulosic biofuel supply
discussed in Section III.D above and estimates of other
non-ethanol renewable fuel supply discussed in Section
IV.B.3, we considered whether the supply of total
238a
biodiesel and renewable diesel would be adequate to
satisfy a requirement of 19.28 billion gallons.103 The
following sections provide our assessment of ethanol
and biodiesel/renewable diesel volumes.
1. Ethanol
Ethanol is the most widely produced and consumed
biofuel, both domestically and globally. Since the beginning of the RFS program, the total volume of renewable fuel produced and consumed in the United States
has grown substantially each year, primarily due to
the increased production and use of corn ethanol.
However, the rate of growth in the supply of ethanol
to the U.S. market has decreased in recent years as
the gasoline market has become saturated with E10,
and efforts to expand the use of higher ethanol blends
such as E15 and E85 have not been sufficient to maintain past growth rates. Although we believe ethanol
use is growing and can continue to grow, the low number of retail stations selling these higher-level ethanol
blends, along with poor price advantages compared to
E10, and a limited number of FFVs, among others, represent challenges to the rate of growth of ethanol as a
transportation fuel in the United States.
In the 2014–2016 final rule we discussed in detail the
factors that constrain growth in ethanol supply and
the opportunities that exist for pushing the market to
103
As noted earlier, “reasonably attainable” volumes may be
less than the “maximum achievable” volumes we would seek to
identify when using the general waiver authority based on a
finding of inadequate domestic supply. It follows that if there are
sufficient reasonably attainable volumes of renewable fuel to
satisfy a total renewable fuel requirement of 19.28 billion gallons,
that there is no basis for a finding of inadequate domestic supply.
239a
overcome those constraints.104 That discussion generally remains relevant for 2017, though we believe that
the supply of ethanol can be somewhat higher in 2017
than in 2016.
Ethanol supply is not currently limited by production and import capacity, which is in excess of 15 billion gallons.105 Instead, the amount of ethanol supplied
is constrained by the following:
Overall gasoline demand and the volume
of ethanol that can be blended into gasoline as E10 (typically referred to as the
E10 blendwall).
The number of retail stations that offer
higher ethanol blends such as E15 and
E85.
The number of vehicles that can both
legally and practically consume E15 and/or
E85.
Relative pricing of E15 and E85 versus
E10 and the ability of RINs to affect this
relative pricing.
The supply of gasoline without ethanol (E0).
The applicable standards that we set under the RFS
program provide incentives for the market to overcome
many of these ethanol-related constraints.
While in the short term the RFS program is unlikely
to have a direct effect on overall gasoline demand or
the number of vehicles designed to use higher ethanol
104
105
80 FR 77456–77465.
“RFA 2016 Annual Industry Outlook,” docket EPA–HQ–
OAR–2016–0004.
240a
blends, it can provide incentives for changes in some
other market factors, such as the number of retail stations that offer higher ethanol blends and the relative
pricing of those higher ethanol blends in comparison
to E10. The RFS program complements other efforts
to increase the use of renewable fuels, such as the
following:
USDA’s Biofuel Infrastructure Partnership (BIP) program which has provided
$100 million in grants for the expansion of
renewable fuel infrastructure in 2016 (supported by additional State matching funds)
USDA’s Biorefinery Assistance Program
which has provided loan guarantees for
the development and construction of
commercial-scale biorefineries with a number of the new projects focused on producing fuels other than ethanol.
The ethanol industry’s Prime the Pump
program, which has committed more than
$45 million to date for retail refueling
infrastructure106
In response to the NPRM, many stakeholders
repeated their views from the 2014–2016 rulemaking
regarding the existence and nature of the E10 blendwall. Ethanol proponents generally regard the blendwall
as a fictional idea created by refiners, and said or
implied that increases in ethanol supply beyond the
blendwall are only limited by refiners’ unwillingness
to invest in the necessary infrastructure. Some also
said that EPA’s approach to setting standards, in
106
“Email dialogue with Robert White on Prime the Pump,”
docket EPA–HQ–OAR–2016–0004.
241a
which constraints on the supply of ethanol are used as
justification for reducing the volume requirement below
the statutory targets, was a self-fulfilling prophecy
that guaranteed that the blendwall would never be
exceeded. Refiners and marketers typically viewed the
constraints associated with the blendwall as representing a firm barrier that could not or should not be crossed,
with costs for necessary infrastructure changes being
prohibitively high and the associated opportunities for
greater profits at retail being inconsequentially low. In
their views, higher level ethanol blends such as E15
and E85 would be negligible in 2017 and standards
that required higher ethanol blends to increase dramatically would compel refiners to reduce domestic supply
of gasoline and diesel or risk non-compliance.
As stated in the 2014–2016 final rule and in the
NPRM, our view of the E10 blendwall falls between
these two viewpoints. We continue to believe that there
are real constraints on the ability of the market to
exceed an average nationwide ethanol content of 10%.
However, these constraints do not have the same
significance at all ethanol concentrations above 10%.
Instead, for the state of infrastructure that can be
available in 2017, the constraints represent a continuum of mild resistance to growth at the first increments above 10% ethanol and evolve to significant
obstacles at higher levels of ethanol. In short, the E10
blendwall is not the barrier that some stakeholders
believe it to be, but neither are increases in poolwide
ethanol concentrations above 10% unlimited in the
2017 timeframe.
We continue to believe that the constraints associated with the E10 blendwall do not represent a firm
barrier that cannot or should not be crossed. Rather,
the E10 blendwall marks the transition from rela-
242a
tively straightforward and easily achievable increases
in ethanol consumption as E10 to those increases in
ethanol consumption as E15 and E85 that are more
challenging to achieve. Comments received in response
to the NPRM provided no compelling evidence that the
nationwide average ethanol concentration in gasoline
cannot exceed 10.0%.
However, we also recognize that the market is not
unlimited in its ability to respond to the standards we
set. This is true both for expanded use of ethanol and
for non-ethanol renewable fuels. The fuels marketplace
in the United States is large, diverse, and complex,
made up of many different players with different, and
often competing, interests. Substantial growth in the
renewable fuel volumes beyond current levels will
require action by many different parts of the fuel
market, and a constraint in any one part of the market
can act to limit the growth in renewable fuel supply.
Whether notable constraints are in the technology development and commercialization stages, as has been the
case with cellulosic biofuels, the development of distribution infrastructure as is the case with ethanol, or in
the distribution and use of biodiesel, the end result is
that these constraints limit the growth rate in the
available supply of renewable fuel as transportation
fuel, heating oil, or jet fuel. These constraints were discussed in detail in the 2014–2016 final rule, and we
believe that the same constraints will operate to limit
supply for 2017 as well.107 Other factors outside the
purview of the RFS program also impact the supply of
renewable fuel, including the price of crude oil and
global supply and demand of both renewable fuels and
their feedstocks. These factors add uncertainty to the
107
See 80 FR 77450.
243a
task of estimating the adequacy of supply of renewable
fuel in the future.
While the constraints are real and must be taken
into account in our evaluation of whether there is adequate supply to meet 19.28 billion gallons of total
renewable fuel, none of those constraints represent
insurmountable barriers to growth. Rather, they are
challenges that are in the process of being addressed
and will be overcome in a responsive marketplace given
enough time and with appropriate investment. The
speed with which the market can overcome these constraints is a function of whether and how effectively
parties involved in the many diverse aspects of renewable fuel suppl respond to the challenges associated
with transitioning from fossil-based fuels to renewable
fuels, the incentives provided by the RFS program, and
other programs designed to incentivize renewable fuel
use.
i. E0
We based the proposed total renewable fuel volume
requirement in the NPRM on the same expectation
from the 2014–2016 final rule regarding supply of E0:
The RFS program would result in all but a tiny portion—
estimated at 200 million gallons—of gasoline to contain at least 10% ethanol. We based this determination on the following two considerations:
1. The RFS program will continue incentivizing the market to transition from E0 to
E10 and other higher level ethanol blends
through the RIN mechanism.
2. Recreational marine engines represent a
market segment that we believe would be
particularly difficult to completely transition from E0 since they are used in a water
244a
environment where there is a greater potential for water contamination of the fuel.
Some consumers are concerned that there
could be a potential for consequent engine
damage following phase separation of the
water and fuel.108
Based on the analysis conducted for the 2014–2016
final rule, it is most likely that any recreational marine
engines refueled at retail service stations (i.e., not at
marinas) would use only E10 since E0 is not typically
offered at retail. Moreover, only a small minority of
recreational marine engines refuel at marinas where
E0 is more likely to be available, catering to that
particular market. In a memorandum to the docket,
we evaluated the information that had been supplied
to us by stakeholders, highlighting the uncertainty in
that information and concluding that about 200
million gallons of E0 was a reasonable estimate of the
volume likely to be consumed by recreational marine
engines.109 In the NPRM, we expressed our belief that
this analysis also reflected reasonable expectations for
2017.
In response to the proposal for the 2017 standards,
some stakeholders said that we had significantly underestimated the volume of E0 used by recreational marine
108
We note that a recent report from the National Renewable
Energy Laboratory calls into question the significance of water
contamination for recreational marine engines. See “Gas becomes
stale before water uptake becomes a concern,” Ethanol Producer
Magazine, September 21, 2016. See also original report “Water
Uptake and Weathering of Ethanol-Gasoline Blends in Humid
Environments,” by Christensen & McCormick, National Renewable Energy Laboratory, September, 2016.
109
“Estimating E0 use in recreational marine engines,” memorandum from David Korotney to docket EPA–HQ–OAR–2015–0111.
245a
engines. However, no new information was provided
that was not already considered in the 2014–2016 final
rule and discussed in the aforementioned memorandum and, as before, no stakeholders provided any data
on actual consumption of E0 by recreational marine
engines. Moreover, the anecdotal information suggesting that most if not all recreational marine engines are
fueled on E0 does not represent an appropriate basis
for increasing our estimate since it was not based on
any form of data and moreover appears highly unlikely
given our expectation that only a small minority of
recreational marine engines refuel at marinas where
E0 is likely to be more prevalent.
Other stakeholders said that we had ignored significant demand for E0 in our determination of the total
volume of ethanol that can be supplied. They pointed
beyond recreational marine engines to other small
engines where there is demand for E0, and to Web
sites like Pure-gas.org, which claim to list more than
11,000 stations which offer E0. Several stakeholders
pointed to a report from EIA suggesting that 5.3 billion
gallons of E0 was consumed in 2015.110 Several refiners reiterated their comments responding to the 2014–
2016 proposal which used EIA data to conclude that
there is ongoing demand for E0 at a level of at least 3%
of the total gasoline pool. This estimate of E0 demand
was the primary basis for their request that the 2017
standards be set in such a way that the poolwide
gasoline ethanol concentration is no higher than 9.7%.
Other than references to data and analyses collected
by EIA, no stakeholder provided any data on actual E0
110
“Almost all U.S. gasoline is blended with 10% ethanol,”
Energy Information Administration, Today In Energy, May 4,
2016.
246a
consumption. With regard to data from EIA, in the
2014–2016 final rule we addressed refiners’ claim that
3% of the gasoline pool has been E0 for several years,
concluding that those estimates were generated from
incomplete EIA gasoline supply data which overestimated the potential demand for E0 at retail.111 Comments from refiners in response to the 2017 proposal
did not provide any new or different information that
would change our conclusions with regard to that 3%
estimate.
With regard to EIA’s more recent estimate that 5.3
billion gallons of E0 was consumed in 2015, we do not
believe that this value represents consumption of E0
at the retail. EIA’s estimate was based on survey data
from most U.S. terminals, which include information
about domestic distribution from the terminal level
and exports of ethanol-free gasoline, with the difference representing domestic disposition. EIA combines
this information with estimates of available ethanol,
assuming that the ethanol is used in a 10% blend with
ethanol-free gasoline. As described in a memorandum
to the docket, our analysis of EIA’s estimate of 5.3
billion gallons of E0 concludes that it would require
E85 volumes significantly higher than the volumes
likely to have been supplied in 2015.112 In our view, the
5.3 billion gallons of E0 estimated by EIA must include
volumes that are blended with ethanol downstream of
terminal prior to dispensing from retail and centralized fleet refueling stations where additional ethanol
blending can and does occur in excess of the blending
used in EIA’s estimate. The calculations are very
111
112
See discussion at 80 FR 77462.
“Ethanol Consumption in 2015 and Estimates of E0 Use,”
memorandum from David Korotney to Docket EPA–HQ–OAR–
2016–0004.
247a
sensitive to the exact volume of total ethanol available
for blending, with EIA and EPA estimated volumes of
total ethanol used differing by about 1 percent. We
believe that EMTS data provides more accurate information on actual use of ethanol in motor fuel than
EIA’s survey data on ethanol production, blending,
imports, and exports because it accounts for every gallon of ethanol produced but not exported, and is verified by the purchaser in the transaction within EMTS.
Based on our analysis, we estimate that E0 consumption at the retail level in 2015 would have been closer
to about 700 million gallons.
Some stakeholders pointed out that it would be difficult for the market to transition about 5 billion gallons
of E0 to E10 within one year. However, since we believe
that actual consumption of E0 in 2015 was much closer
to 700 million gallons than 5.3 billion gallons, continuing to transition away from E0 since then to 200 million gallons of E0 by the end of 2017 is achievable. As
a result, we continue to believe that 200 million gallons of E0 is a reasonable value to assume for purposes
of assessing the adequacy of supply of total renewable
fuel, based on our prior assessment that this volume
dedicated to recreational marine engine use may not
be significantly influenced by the standards we set in
this time period, and our expectation that the RFS program will continue to incentivize all but this small
portion of the gasoline pool to be blended with ethanol.
Stakeholders representing boat owners expressed
concern that by including only 200 million gallons of
E0 in the proposed derivation of maximum achievable
total renewable fuel volumes, EPA anticipated effectively limiting the availability of E0 to 200 million
gallons. This is not the case. The standards that EPA
sets are not specific to ethanol nor to specific ethanol
248a
blends. Once the standards are set, the market has the
flexibility to choose the mix of fuel types used to meet
those standards. If, for instance, the demand for E0 in
2017 is higher than 200 million gallons, the market
can compensate by providing higher volumes of E15
and/or E85, or additional non-ethanol renewable fuels.
ii. E15
In the NPRM, we proposed that a total ethanol volume of 14.4 billion gallons could be reached in 2017
based on the expectation that somewhat larger increases
in ethanol supply were possible in 2017 than we had
estimated for 2016. We did not provide specific estimates of E15 or E85 use in 2017, but instead said that
we generally expected the RFS program to influence
sales of E0, E15, and E85 in such a way as to produce
this increase in ethanol volume. For this final rule, we
have undertaken a more detailed estimate of the volumes of E15 and E85 that are possible in 2017, so as
to more confidently assess whether there is adequate
supply to reach a total renewable fuel volume requirement of 19.28 billion gallons.
Most comments in response to the NPRM repeated
viewpoints they had expressed in response to the
2014–2016 proposal. Refiners and their associations,
as well as parties representing fuel marketers and
retail, expressed doubt that the number of stations offering E15 could increase significantly in 2017 and pointed
to vehicle warranties that they believed would hinder
many owners of 2001+ model year vehicles from refueling on E15. They also repeated their concerns about
engine damage and liability for misfueling. Ethanol
proponents generally pointed to the large number of
in-use vehicles that are legally permitted to use E15
and information suggesting that many existing retail
stations are already compatible with E15, or can be
249a
inexpensively upgraded. They also pointed to incentives for expanded infrastructure provided by programs
such as USDA’s Biofuels Infrastructure Partnership
(BIP) program and the ethanol industry’s Prime the
Pump program. A more detailed discussion of our
views of these comments can be found in the 2014–
2016 final rule and in the Response to Comments document for this final rule.113
Consistent with our assessment for the 2014–16
final rule, we believe that neither the number of vehicles that are legally permitted to use E15, nor the
number of owners of such vehicles who would choose
to use it, are the predominant factors in determining
the volume of E15 that is reasonably attainable in
2017. Instead, we believe that it is the number of retail
stations offering E15 in 2017 that is more likely to
determine how much E15 is actually consumed. The
number of retail stations registered to offer E15 has
grown to about 400 in the fall of 2016 based on information collected by the RFG Survey Association, more
than doubling from the previous year. However, this is
still a very small fraction of the approximately 150,000
retail stations currently operating. Based on comments
received from retail station owners and their associations, this low number of retail stations offering E15 is
most likely due to liability concerns and low expectations for a return on an investment in new or upgraded
infrastructure.
We do not believe, based on past experience, that the
core concerns retailers have with liability over equipment compatibility and misfueling would change if the
RFS volume requirements were increased significantly. Similarly, while higher RFS volume require113
See discussion at 80 FR 77462–77464.
250a
ments could make it incrementally more attractive for
retailers to upgrade infrastructure to offer E15, the
concerns they expressed in their comments about high
capital costs and opportunities for return on their
investment would remain. As a result, setting higher
volume requirements would be unlikely to result in
dramatic increases in the number of additional retail
stations offering E15 in 2017 beyond those that may
be upgraded through existing grant programs. As a
result, we do not believe that E15 infrastructure expansion can occur on the much larger scale and faster
timeframe that ethanol proponents believe it can. However, we do believe that retail infrastructure can and
will change to offer more E15 in 2017. We have estimated the expansion that is possible in 2017 based on
information on both the BIP and Prime the Pump programs, as well as an expectation that independent
efforts to expand infrastructure will continue. As
described in a memorandum to the docket, we believe
that the number of stations will increase during the
course of the year, and that an annual average of about
1,640 retail stations will be able to offer E15 in 2017.114
Since actual experience with E15 sales is so limited,
and commenters provided little information on actual
E15 sales volumes, we have made an estimate of possible E15 use in 2017 using the same methodology that
was presented in the 2014–2016 final rule, supplemented by additional information about E15 that is
expected to be supplied by terminals.115 That estimate
114
“Projections of retail stations offering E15 and E85 in
2017,” memorandum from David Korotney to docket EPA–HQ–
OAR–2016–0004.
115
“Estimates of E15 and E85 volumes in 2017,” memorandum
from David Korotney to docket EPA–HQ–OAR–2016–0004.
251a
was based on the following equation, which was also
used in the 2014–2016 final rule:
E15 volume = (Total gasoline throughput per station)
(Number of stations offering E15) (Fraction
of total gasoline sales which are E15)
We have updated the values used in this calculation
based on comments provided by stakeholders and additional information that has become available since
release of the NPRM. First, we have updated the number of retail stations that may offer E15 in 2017, as
discussed above. Second, some stakeholders said that
retail stations being targeted under the BIP program
had greater total annual gasoline sales than average,
such that it would be inappropriate to assume that the
total gasoline throughput per retail service station in
the above equation is equal to the nationwide average,
currently about 0.95 million gallons per station per
year. Available information on the BIP program does
not include gasoline throughput, but larger retail stations would be more likely to produce the matching
funds necessary as a condition of receiving BIP grant
funds. One stakeholder that is actively and directly
working with many of the retailers using funds from
the BIP and Prime the Pump programs indicated that
the average total gasoline throughput for affected
retail stations is 2.8 billion gallons per year. Therefore,
we have used this value in our determination of E15
supply for 2017. Further discussion can be found in a
memorandum to the docket.116
Finally, in the 2014–2016 final rule we used a value
of 50% for the fraction of total gasoline sales which are
E15 at stations offering both E10 and E15 based on
the expectation that E10 and E15 could be priced
116
Ibid.
252a
equally on a volumetric energy basis. While we continue to believe that 50% is possible, a number of refiners pointed out reasons that 50% may be too high in
the near term, including the fact that there are likely
to be fewer dispensers at a given retail station offering
E15 than those offering only E10, and customer familiarity with E10. One party indicated that in Iowa in
2015, per-station E15 sales were 15% of per-station
E10 sales, though the data on which this conclusion
was based did not rely on retail stations selling both
E10 and E15; the per-station estimate for E10 was
based on all stations offering E10, regardless of whether
they also offered E15. Not only are the Iowa data not
necessarily representative of stations offering both
E10 and E15, we have no information to indicate
whether the experience in Iowa is representative of
conditions that could exist under the increasing RFS
standards in 2017. Nevertheless, we agree that the
fraction of total gasoline sales which is E15 at stations
offering both E15 and E10 is likely to be considerably
less than 50% for the reasons described earlier (e.g.,
number of dispensers offering E15 at a given station,
consumer unfamiliarity with E15), at least in 2017.
Since we only have one source of data upon which to
base our estimate, we are using that 15% value in our
assessment.
Although E15 has historically been produced at
retail stations in blender pumps, since release of the
NPRM we have become aware of new activities to
produce E15 at terminals.117 This E15 could be used in
retail equipment that has been certified to be compatible with E15, and so would expand the use of E15
beyond that available through blender pumps, includ117
“HWRT & RFA Announce First-Ever Offering of Pre-blended
E15,” docket EPA–HQ–OAR–2016–0004.
253a
ing those targeted by the BIP and Prime the Pump
programs. Based on currently available information,
four out of the approximately 1,400 terminals in the U.S.
would produce E15 in 2017, and we expect that E15
production at those four terminals would be small in
comparison to E10 production. As described in a memorandum to the docket, we estimate the E15 produced
through terminals would be 41 million gallons in 2017.118
Based on the above discussion, we have estimated
that total E15 supply in 2017 could reach 728 million
gallons, resulting in about 38 million gallons of ethanol more than would be supplied if that portion of the
gasoline pool were E10. We have included this in our
discussion of total ethanol volumes in Section V.B.1.iv
below.
iii. E85
As described previously, the NPRM did not provide
specific estimates of E15 or E85 use in 2017, but
instead indicated that we generally expected the RFS
program to influence sales of E0, E15, and E85 in such
a way as to produce a total ethanol supply of 14.4 billion gallons. Nevertheless, stakeholders provided comments on a variety of topics related to the estimation
of achievable volumes of E85.119 Many of these comments
focused on an analysis of the relationship between E85
sales volumes and E85 price discount derived from pub118
“Estimates of E15 and E85 volumes in 2017,” memorandum
from David Korotney to docket EPA–HQ–OAR–2016–0004.
119
We note that, in the 2014–2016 final rule, the estimation
of E85 volumes was made in the context of determining the
volume that constituted inadequate domestic supply under our
general waiver authority. For this final rule, we are using the
cellulosic waiver authority alone, and are estimating reasonably
attainable volumes of E85.
254a
lically available data from six states, which was provided with the 2014–2016 final rule.120
As for many other aspects of this rule, stakeholders
were strongly divided on the volumes of E85 that are
achievable in 2017. Refiners typically said that E85
volumes are likely to reach little more than around 100
million gallons in 2017 based on their own estimates
of E85 in previous years using data collected by EIA
from refiners, blenders, and ethanol production facilities. For instance, refiners suggested that E85 use in
2015 reached only 87 million gallons. However, as discussed in the 2014–2016 final rule, the EIA sources on
which this estimate was based do not capture all E85
that is actually used; not all production at terminals,
ethanol production facilities, or blenders with less than
50,000 barrels of product storage capacity are included,
nor is E85 captured which is produced using reformulated gasoline or natural gasoline as the petroleum
based component. Also, reported E85 production at
ethanol production facilities is likely to represent net
rather than total finished fuel production given the
occasional negative values reported in the past.121
These stakeholders provided no new information on
historical E85 supply beyond what these EIA sources
120
“Correlating E85 consumption volumes with E85 price,”
memorandum from David Korotney to docket EPA–HQ–OAR–
2015–0111.
121
Reported values for ethanol production facilities represent
net finished fuel produced. Insofar as finished fuel brought into
the facility (i.e., gasoline) exceeds finished fuel produced by the
facility (i.e., E85), a net negative value will result. This would
occur if gasoline brought into the facility is used as a denaturant
only, or as both a denaturant and in the production of E85. As a
result, the values reported by EIA do not capture actual E85
produced and made available by these facilities, which would be
the relevant value to use in our assessment.
255a
capture. As described in a memorandum to the docket,
our own estimate of actual E85 use in 2015 based on
E85 supply data from six states is approximately 186
million gallons.122 Moreover, we also do not believe it
would be appropriate to merely extrapolate 2017 E85
supply from trends in the past several years as some
stakeholders suggested. Doing so would ignore the ability of the market to respond to the standards that we
set.
In contrast, ethanol proponents said that E85 volumes could reach at least 500 million gallons in 2017,
and some provided estimates considerably higher. Several pointed to E85 supply projections from EIA’s
Annual Energy Outlook 2016 (AEO2016), which projects 735 million gallons for 2017. However, we do not
believe that the AEO is an appropriate basis for projecting E85 supply in 2017 for the purposes of setting
the applicable volume requirements under the RFS
program. For instance, the same modeling that projected 735 million gallons for 2017 also projected 326
and 508 million gallons, respectively, for 2014 and 2015.
These volumes are far higher than what we believe the
actual supply was in these years.123 And AEO2016
projects that total ethanol use in 2017 would be 13.8
billion gallons, far lower than the 14.4 billion gallons
that we proposed as the maximum achievable, and
also considerably lower than EIA’s own projections for
2017 in their Short-Term Energy Outlook (STEO). As
the STEO projections are based on more current information and are focused on more near-term outcomes,
122
“Final estimate of E85 consumption in 2015,” memorandum
from David Korotney to docket EPA–HQ–OAR–2016–0004.
123
For instance, as described in the 2014–2016 final rule (80
FR 77460), we estimate that E85 use in 2014 was about 150 mill
gal.
256a
and the STEO also forms the basis for the gasoline and
diesel demand projections that EIA has indicated should
be used for determining the applicable percentage
standards, we do not believe that AEO is an appropriate basis for estimating the E85 supply in 2017 that is
reasonably attainable, nor, as another commenter suggested, total gasoline energy demand for 2016. We
have used the STEO for the projection of 2017 total
gasoline demand, combined with our own projections
of total ethanol supply based on our estimates of reasonably attainable volumes of E15 and E85, along with
a small amount of E0.
For those stakeholders who provided detailed comments on how E85 supply might best be projected for
2017, those comments typically focused on three areas:
The number of flex-fueled vehicles (FFVs)
in the 2017 fleet that can use E85
The retail infrastructure that can be made
available in 2017 to supply E85 to FFVs
The degree to which E85 sales can be influenced by the E85 price discount relative to
E10
We continue to believe that the number of FFVs in
the fleet is not the controlling constraint on the use of
E85. According to AEO2016, the number of FFVs in
the fleet in 2017 is expected to be about 21 million.124
These vehicles could use up to 13 billion gallons of E85
if all of them had access to retail stations offering it
and all FFV owners chose to refuel on E85 instead of
E10. We acknowledge that a larger percentage of FFVs
in the fleet could increase the volume of E85 consumed,
but in the short term we believe that it is the relatively
124
Table 40, “Light-Duty Vehicle Stock by Technology Type.”
257a
very small number of retail stations offering E85 that
is operating as the primary constraint on the volumes
of E85 sold, and to a lesser extent the relative price of
E85 and E10.
Many stakeholders provided comments on how the
number of retail stations offering E85 could grow
through the end of 2017. Most pointed to a combination of USDA’s Biofuels Infrastructure Partnership
(BIP) program, the ethanol industry’s Prime the Pump
program, and ongoing efforts independent of these two
programs. Parties representing gasoline marketing and
retail, in contrast, generally repeated the concerns
that they raised in the 2014–2016 final rule about
costs for new infrastructure and low expected profit
margins in support of their view that the number of
retail stations offering E85 would grow slowly. Several
stakeholders pointed to specific examples of retail
stations that had stopped offering E85 due to poor
sales.
Based on the information provided by stakeholders
and other information that became available following
release of the NPRM, we believe that the BIP and
Prime the Pump programs will drive nearly all growth
in E85 stations through the end of 2017, with far less
growth occurring through independent efforts. As
described in a memorandum to the docket, we believe
that an annual average of about 4,300 retail stations
can offer E85 in 2017.125 This is a significant increase
in comparison to the 3,200 that we projected would
offer E85 in 2016 in the 2014–2016 final rule, but still
125
“Projections of retail stations offering E15 and E85 in 2017,”
memorandum from David Korotney to docket EPA–HQ–OAR–
2016–0004.
258a
a relatively small number of stations compared to the
estimated 150,000 retail stations nationwide.
In order to estimate reasonably attainable sales volumes of E85 in 2017, it is also necessary to estimate
the volume of E85 likely to be sold at each retail station
that offers it. Recognizing this, stakeholders provided
comments on the aforementioned analysis of the relationship between E85 sales volumes at retail and E85
price discount derived from publically available data
from six states. Refiners generally dismissed the value
of the data used in this analysis, saying that the uncertainty within the data and questions about its representativeness for the nation as a whole made it an
improper basis for future projections. They instead
suggested that E85 use in 2017 should be based only
on an extrapolation of E85 supply trends from the previous few years. We disagree. The data used for the
analysis demonstrated statistically significant correlations between E85 sales volumes and E85 price discounts, and represented between 21% and 31% of all
stations in the U.S. which offered E85.126 Moreover,
their suggested extrapolation from historical data would
insufficiently account for the influence of both the RFS
program itself and programs such as BIP and Prime
the Pump, and would also be based on historical estimates of E85 supply using EIA data that, as described
above, we believe are likely to be inaccurate.
Ethanol proponents recognized the value of the available data in developing correlations between E85 sales
at retail and E85 price discounts. However, they provided critiques of the analyses we had conducted for
the 2014–2016 final rule, and they also had alternative views on the application of the resulting correla126
Range depends on the month and year.
259a
tions. Comments provided by these stakeholders generally fell into broad areas:
The data should be represented by nonlinear rather than linear correlations
Estimates of E85 use derived from the
correlations should be based on substantial extrapolations beyond the limits of the
data, i.e. using much higher E85 price discounts than have occurred in the past
Some stakeholders conducted their own analyses of
the data wherein they employed additional statistical
techniques to attempt to more precisely determine the
nature of the relationship between E85 sales volumes
and E85 price discounts. These included such things
as adding seasonal and annual categorical variables
into the correlations and an investigation into different nonlinear functional forms.
In light of the comments provided by these stakeholders, we determined that the analyses conducted
for the 2014–2016 final rule should be updated. Not
only is additional data now available for the six states
included in the analyses, but more rigorous statistical
methods can be employed to more precisely determine
the relationship between E85 sales volumes and E85
price discount, including whether a nonlinear correlation is appropriate. As described in a memorandum to
the docket, our revised analyses indicate that a weak
nonlinear relationship can be discerned in the data,
and that it does provide a small increase in the explanatory power of the curve fit.127
127
“Updated correlation of E85 sales volumes with E85 price
discount,” memorandum from David Korotney to docket EPA–
HQ–OAR–2016–0004.
260a
In addition to an estimate of the number of retail
stations that may offer E85 in 2017, the use of a
correlation between E85 sales volumes and E85 price
discount to estimate reasonably attainable volumes of
E85 for 2017 requires that we estimate an E85 price
discount that would be reasonable for 2017. Again,
stakeholders were strongly divided on what E85 price
discount may be attainable in 2017. Refiners typically
said that an E85 price discount beyond energy parity
(about 22% below the price of E10) was not supportable based on historical data and pointed to EPA’s
analyses showing that a sizable portion of the RIN
value is not passed on to retail customers, diluting the
impact of RIN prices on E85 prices. Ethanol proponents instead said that historical E85 price discounts
should not be used as a gauge of what future E85 price
discounts could be under the influence of higher RFS
program standards. They discounted the limitations
associated with the pass-through of RIN values to
retail customers, arguing that if EPA set the standards high enough, the resulting higher RIN prices
would result in significantly discounted retail pricing
for E85 at the retail level. Some commenters presented
examples of individual stations or regions where it
appeared the RIN value was being passed-through to
a greater degree to support their statements, however
EPA does not believe these examples are representative of retailer behavior across the country.128
There is no straightforward mechanism for precisely
identifying an E85 price discount for use in assessing
2017 ethanol supply. While some stakeholders provided
examples of E85 price discounts that could be reached
under specific assumed RIN prices and assumed RIN
128
For a further discussion of these comments, see Section
2.3.8.2 of the Response to Comment document.
261a
value pass-through to retail customers, such examples
were purely speculative and provided no method for
determining the E85 price discount that is likely to be
reasonably attainable in 2017 given the E85 retail
prices we have observed to date and the history of the
fuels market.
In order to identify an E85 price discount that could
be reasonably be assumed for the nation as a whole in
2017, we continue to believe that an investigation of
E85 price discounts reached in the past is both less
speculative than the suggestions made by ethanol proponents in their comments and more consistent with
commonly accepted approaches to data analysis. However, we also do not believe that the average levels
achieved in the past are sufficiently representative of
what could be expected to occur in the future under the
influence of the RFS program. As described in a memorandum to the docket that we published with the NPRM,
the monthly average E85 price discount has rarely
exceeded energy parity (about 22%), and the highest
12-month average retail E85 price discount has been
significantly lower.129
129
“Estimating achievable volumes of E85,” memorandum from
David Korotney to docket EPA–HQ–OAR–2016–0004. Note that
this memorandum was published with the NPRM on May 31,
2016, and with the exception of the discussion of historical E85
price reductions is largely supplanted by memoranda published
with this final rule. See in particular “Estimates of E15 and E85
volumes in 2017,” memorandum from David Korotney to docket
EPA–HQ–OAR–2016–0004.
262a
TABLE V.B.1.iii–1—E85 PRICE DISCOUNTS
BETWEEN 2012 AND EARLY 2016
Fuels
E85prices.com
AAA
Institute
Highest
21.1%
23.7%
24.1%
E85 price (May 2015)
(Oct 2014) (Apr 2015).
discount
18.7%
in a single
(Oct 2014–
month
Sep 2015).
Highest
16.0%
19.6%
24.1%
12-month (Sep 2014–
(Sep 2014– (Apr 2015).
average
Aug 2015).
Aug 2015).
18.7%
E85 price
(Oct 2014–
discount
Sep 2015).
In that memorandum we indicated our belief that
achieving energy parity for a full year would be unprecedented, but appears to be within the capabilities of
the market given the historical values shown above.
E85 price discounts higher than energy parity that
were suggested by some stakeholders in their comments have not been achieved in the past for any
notable length of time, and thus, we believe, are not
likely for all of 2017. They may, however, occur in
future years as the number of retail stations offering
E85 increases and competition between them drives
E85 prices down. For the purposes of this final rule,
we have used an E85 price discount of 22% in estimating the supply of E85 in 2017.
Some stakeholders pointed to a statement in the
NPRM which said “. . . an increase in the nationwide
average E85 price reduction to 30% would be unprecedented,” and then argued that EPA had not provided
any justification for expecting this level to be sustaina-
263a
ble for a full year. We not that E85 price discounts
have reached 30% in the past, albeit locally and for
short time periods. However, we did not propose using
an E85 price discount of 30% in the determination of
the proposed 2017 volume requirement for total renewable fuel, but only provided it as one of several examples for how the market might respond.
130
Combining the updated correlation between E85
sales volumes and E85 price discounts with estimates
for the number of retail stations that can offer E85 in
2017 and a reasonably attainable E85 price discount
of 22%, we have determined that supply of about 275
million gallons of E85 is reasonably attainable in 2017,
resulting in about 182 million gallons of ethanol more
than would be supplied if that portion of the gasoline
pool were E10. This level of E85 supply is an increase
of almost 40% in just one year from the 200 million
gallons that we believed could be reached in 2016,
primarily reflecting the significant increase in the
number of stations projected to offer E85 in 2017 as a
result of USDA’s BIP program and the ethanol industry’s Prime the Pump program.
iv. Total Ethanol
The total supply of ethanol in 2017 is a function of the
respective volumes of E10, E15, and E85, while accounting for some E0. Assuming that the total demand for
gasoline energy is independent of the amounts of each
of these types of fuel, estimating the supply of E0, E15,
and E85 that are attainable can be used to derive the
supply of E10.
Several stakeholders commented that we should use
a more recent version of EIA’s Short-Term Energy
130
See discussion at 81 FR 34790.
264a
Outlook (STEO) than the April, 2016 version we used
in the NPRM to estimate gasoline demand in 2017. We
agree that we should use updated EIA data. For this
final rule we have used the October, 2016 version,
which projects a total gasoline energy demand of 17.29
Quadrillion Btu.131 Based on estimates of E0, E15, and
E85 supply for 2017 as discussed in previous sections,
the E10 volume and resulting total ethanol supply can
be calculated.
TABLE V.B.1.iv–1—GASOLINE VOLUMES
USE TO DETERMINE REASONABLY
ATTAINABLY ETHANOL SUPPLY IN 2017
Fuel volume
(mill gal)
E0 ...............
E10 .............
E15 .............
E85 a ..........
Total ...........
200
142,480
728
275
143,683
Ethanol
volume
(mill gal)
0
14,248
109
204
14,561
Energy
(Quad Btu)
0.025
17.151
0.086
0.026
17.288
Based on this assessment, we estimate an ethanol
supply for 2017 of 14.56 billion gallons. While the
market will ultimately determine the extent to which
compliance with the annual standards is achieved
through the use of greater volumes of ethanol versus
other, non-ethanol renewable fuels, we nevertheless
believe that this ethanol volume represents a reasona131
Derived from Table 4a of the STEO, converting consumed
gasoline and ethanol projected volumes into energy using conversion factors supplied by EIA. http://www.eia.gov/forecasts/steo
/archives/oct16.pdf.
Excludes gasoline consumption in Alaska. For further details,
see “Calculation of final % standards for 2017” in docket EPA–
HQ–OAR–2016–0004.
265a
bly attainable level that takes into account the ability
of the market to respond to the standards we set and
the constraints to fuel supply that we have noted.
One stakeholder said that EIA’s projections of future
gasoline demand as provided in the STEO have been
too low in previous years, and that EPA should account
for this underestimate when making projections of the
volume of ethanol that can be achieved in 2017. We
investigated this issue and determined that while EIA
projections of future gasoline demand do contain uncertainty, they are not consistently above or below actual
gasoline demand.132
In response to the NPRM, some stakeholders reiterated their concerns from the 2014–2016 final rule that
EPA’s methodology rewarded obligated parties for
their recalcitrance in not investing in the infrastructure needed to substantially increase ethanol use above
the E10 blendwall. In taking these positions, stakeholders cited both the statutory requirement that obligations be placed on “refineries, blenders, and importers, as appropriate” and EPA’s regulations which (with
limited exceptions) further narrow the applicability of
the obligations to producers and importers of gasoline
and diesel. As described in the 2014–2016 final rule,
we agree that the statutory language, in combination
with the regulatory structure, generally places the
responsibility on producers and importers of gasoline
and diesel to ensure that transportation fuel sold or
introduced into commerce contains the required volumes of renewable fuel. Obligated parties have a variety
of options available to them, both to increase volumes
in the near term and the longer term. The standards
132
“Accuracy of STEO gasoline demand projections,” memorandum from David Korotney to docket EPA–HQ–OAR–2016.
266a
that we are establishing today reflect both the responsibility placed on obligated parties as well as the shortterm activities available to them, and we expect
obligated parties to be taking actions now that will
help to increase renewable fuel volumes in future years.
However, as pointed out by some refiners in response
to the NPRM, this general responsibility does not
require obligated parties to take actions specific to E15
and/or E85 infrastructure, as the RFS program does
not require any volumes of ethanol specifically. We
continue to believe that as obligated parties procure
and blend renewable fuels into transportation fuel, or
purchase RINs from those who do so, the demand for
RINs will drive demand for renewable fuel, thereby
stimulating every participant in the fuels industry,
including obligated parties themselves, to increase
their activities to supply it.133 Moreover, the reductions
in statutory volumes reflected in this action are largely
the result of the inability to date of renewable fuel producers to commercialize the volumes of cellulosic biofuel
envisioned in the statute. This fact cannot reasonably
be attributed to actions or inactions of obligated parties.
One stakeholder said that the EPA should target a
poolwide gasoline ethanol content of less than 10% in
part because blenders need a buffer to account for
uncertainty associated with ethanol content testing
and downstream mixing in the fungible distribution
system. This stakeholder suggested that blenders have
historically aimed to blend at less than 10% ethanol,
and that as a result EPA should set standards con133
The EPA Administrator signed the Proposed Denial of Petitions for Rulemaking to Change the RFS Point of Obligation on
November 10, 2016. More information can be found at https://www.
epa.gov/renewable-fuel-standard-program/response-petitions-re
consideration-rfs2-rule-change-point-obligation.
267a
sistent with this practice. We investigated this issue
using survey data collected by the Alliance of Automobile Manufacturers for 2011–2015 and determined
that the average ethanol content of all gasoline that
contained more than de minimis levels of ethanol was
9.80%.134 This estimate is based on the use of ASTM
test method D–5599, which measures only the alcohol
portion of the gasoline, not any denaturant that would
have been included with the ethanol before it was
blended into gasoline. Since the denaturant portion of
ethanol is typically about 2%, ethanol that is blended
into gasoline contains about 98% ethanol.135 When
blended into gasoline, therefore, the E98 would result
in a gasoline-ethanol blend containing about 9.8% pure
ethanol, or 10.0% denatured ethanol. Based on this
investigation, we have determined that it is appropriate to continue assuming that the denatured ethanol
content of E10 is 10%.
2. Biodiesel and Renewable Diesel
While the market constraints on ethanol supply are
readily identifiable, it is more difficult to identify and
assess the market components that may limit potential
growth in the use of all qualifying forms of biodiesel
and renewable diesel in 2017. Therefore, as discussed
in the introduction to Section V.B, after estimating the
supply of ethanol in 2017, and taking into account the
estimates of non-ethanol cellulosic biofuel supply discussed in Section III.D above and estimates of other
non-ethanol renewable fuel supply discussed in Section
IV.B.3, we considered whether the supply of total bio134
Under the rounding method required under 40 CFR 80.9,
ethanol concentrations of between 8.6% and 10.5% inclusive would
qualify for the 1psi waiver.
135
See definition of “renewable fuel” at 40 CFR 80.1401.
268a
diesel and renewable diesel would be adequate to satisfy a requirement of 19.28 billion gallons.
In Section V.A we described how use of the cellulosic
waiver authority to provide a volume reduction for total
renewable fuel that equals that provided for advanced
biofuels yields a volume of 19.28 billion gallons. In
addition to the ethanol volume discussed in Section
V.B.1.iv above, cellulosic biogas can also contribute to
this total volume of renewable fuel, as described more
fully in Section III.D. While other renewable fuels such
as naphtha, heating oil, butanol, and jet fuel can be
expected to continue growing over the next year, collectively, we expect them to contribute considerably less
than ethanol to the total volume of renewable fuel that
can be supplied in 2017. These were discussed in
Section IV.B.3. Based on these estimates of supply,
about 2.9 billion gallons of biodiesel and renewable
diesel would be needed in order to meet a total renewable fuel volume requirement of 19.28 billion gallons.
269a
TABLE V.B.3–1—DETERMINATION OF
VOLUME OF BIODIESEL AND RENEWABLE DIESEL
NEEDED IN 2017 TO ACHIEVE 19.28 BILLION
GALLONS OF RENEWABLE FUEL
[Million ethanol-equivalent gallons except as noted]
Total renewable fuel volume .................
Ethanol ..................................................
Non-ethanol cellulosic biofuel ...............
Other non-ethanol renewable fuelsa .....
Biodiesel and renewable diesel needed
(ethanol-equivalent volume/physical
volume) ..................................................
19,280
14,561
299
50
4,370/2,819
As discussed in the final rule establishing the RFS
standards for 2014–2016, there are several factors that
may, to varying degrees and at different times, limit
the growth of biodiesel and renewable diesel, including
local feedstock availability, production and import
capacity, and the ability to distribute, sell, and use
increasing volumes of biodiesel and renewable diesel.
We continue to believe that the supply of biodiesel and
renewable diesel as transportation fuel in the United
States, while growing, is not without limit.
In the proposed rule we discussed the current status
of each of a number of the factors that impact the
supply of biodiesel and renewable diesel used as transportation fuel in the United States. We received a number of comments on our assessment of these factors.
Some of these comments supported the proposed findings in the NPRM and agreed that EPA had sufficiently accounted for the factors that may constrain
the growth of biodiesel and renewable diesel in 2017,
a
Includes naphtha, heating oil, butanol, and jet fuel. See further discussion in Section IV.B.3.
270a
while others argued that EPA had overstated these
constraints and the degree to which they would limit
the supply of biodiesel and renewable diesel in 2017. As
stated in our proposed rule, we expect that the growth
in the supply of biodiesel and renewable diesel will
largely be driven by incremental developments across
the marketplace to steadily increase volumes. However, after a careful review of the information submitted as comments on our proposed rule, we believe
that the reasonably attainable supply of biodiesel and
renewable diesel in 2017 is higher than we had proposed.
Based on our assessment of the various factors which
affect the supply of biodiesel and renewable diesel, we
have determined that 2.9 billion gallons of biodiesel
and renewable diesel (including both advanced and
conventional biofuel) can be reasonably attained in
2017, up from the 2.5 billion gallons that was projected
for 2016. This volume is significantly higher than the
previously established BBD standard of 2.0 billion
gallons for 2017, as we believe additional volumes of
both conventional and advanced biodiesel and renewable diesel can be supplied to the United States in 2017
(see Section VI for further discussion of the BBD standard). The following sections discuss our expectations for
developments in key areas affecting the supply of biodiesel and renewable diesel in 2017.
i. Feedstock Availability
In previous years, the primary feedstocks used to
produce biodiesel and renewable diesel in the United
States have been vegetable oils (primarily soy, corn,
and canola oils) and waste fats, oils, and greases. We
anticipate that these feedstocks will continue to be the
primary feedstocks used to produce biodiesel and renewable diesel in 2017. Global supplies of these oils are
271a
significant, however they are expected to increase relatively slowly over time, as vegetable oil production
increases primarily with increases in crop yields and
the remaining untapped supply of recoverable waste
oils diminishes. Additional supplies of feedstocks could
be produced by increasing the planted acres of oilseed
crops (soy, canola, etc.), but with the exception of palm
oil most vegetable oils are produced as a co-product of
the production of animal feed and increased demand for
vegetable oil is unlikely to result in a significant increase
in oilseed crop planting absent growing demand for the
animal feed. While some have suggested that industries that compete with the biodiesel and renewable
diesel industry for renewable oil feedstocks will turn
to alternative feedstock sources, resulting in greater
feedstock availability for biodiesel and renewable
diesel producers, such a shift in renewable oil feedstock
use would not result in an increase in the total available supply of renewable oil feedstocks as those volumes
will have to be backfilled. As a result, this would not
alter the fundamental feedstock supply dynamics for
biodiesel and renewable diesel production.
We anticipate that there will be a modest increase
in the available supply of feedstocks that can be used
to produce biodiesel and renewable diesel in 2017. Oil
crop yield increases over the next few years are expected
to be relatively modest, and significant increases in
the planted acres of oil crops are expected to be limited
by competition for arable land from other higher value
crops and demand for the animal feed co-products produced by most oilseed crops.136 The recovery of corn oil
136
Because most oilseed crops are grown primarily to provide
livestock feed, the planted acres of these crops are expected to
increase in response to demand for livestock feed rather than
demand for renewable vegetable oils.
272a
from distillers grains and the recovery of waste oils are
already widespread practices, limiting the potential
for growth from these sectors compared to what has
been able to occur over recent years as these new markets were being tapped. In light of this, we do not
believe that the availability of biodiesel and renewable
diesel feedstocks is without limit. It is also possible
that biodiesel production at some individual facilities,
especially those built to take advantage of low-cost,
locally available feedstocks, may be limited by their
access to affordable feedstocks in 2017, rather than
their facility capacity, even if the global supply of feedstocks is sufficient to enable additional production.
As discussed in further detail in Section IV.B.2, the
availability of qualifying advanced biodiesel and renewable diesel feedstocks may also be limited (even if the
total supply of feedstocks is sufficient), and large
increases in advanced biodiesel and renewable diesel
demand could lead to significant feedstock substitution rather than increased production of advanced feedstocks. Unreasonably high demand for biodiesel and
renewable diesel could also cause undesirable market
disruptions. Large increases in the available supply of
biodiesel and renewable diesel in future years will
likely depend on the development and use of new, highyielding feedstocks, such as algal oils or alternative
oilseed crops. Based on currently available information,
we believe that the availability of feedstocks (including
both feedstocks that can be used to produce advanced
and conventional biodiesel and renewable diesel) is
unlikely to significantly limit the supply of total biodiesel and renewable diesel used for transportation
fuel in the United States in 2017, when considering
the standards we are establishing in this rule. This
is largely the case because we believe that other constraints, discussed below, will likely constrain the distri-
273a
bution and use of biodiesel and renewable diesel before
the feedstock limits have been reached.
ii Biodiesel and Renewable Diesel Production Capacity
The capacity for all registered domestic biodiesel production facilities is approximately 3.5 billion gallons.137
The capacity for all registered domestic renewable
diesel production facilities is approximately 0.7 billion
gallons.138 Active production capacity is lower, however, as a number of registered facilities were idle in
2015 and 2016. The capacity for all domestic biodiesel
and renewable diesel production facilities that generated RINs in 2015 or 2016 is approximately 3.1 billion
gallons.139 While idled production facilities may be
brought online, doing so would likely require sufficient
time to re-staff the production facilities, make any necessary repairs or upgrades to the facility, and source
the required feedstocks. Additionally, there are many
factors that may limit biodiesel or renewable diesel
production at any given facility to a volume lower than
the facility capacity.140 As with feedstock availability,
we do not expect that production capacity at registered
facilities will limit the supply of biodiesel/renewable
diesel for use as transportation fuel in the United
States in 2017. Foreign registered biodiesel and renewable diesel facilities represent a significant volume of
137
‘‘Biodiesel and Renewable Diesel Registered Capacity
(October 2016)”, Memorandum from Dallas Burkholder to EPA
Docket EPA–HQ–OAR–2016–0004.
138
Ibid.
139
Ibid.
140
Due to the relatively low capital cost of biodiesel production
facilities, many facilities were built with excess production capacity that has never been used.
274a
additional potential production that could be made
available to markets in the United States. While the
total registered production capacity of foreign biodiesel
and renewable diesel is significant, supply of biodiesel
and renewable diesel from these facilities in 2017 may
be impacted by the capacity to import these fuels,
discussed in the following section.
iii Biodiesel and Renewable
Import Capacity
Diesel
Another important market component in assessing
biodiesel and renewable diesel supply is the potential
for imported volumes and the diversion of domestically
produced biodiesel and renewable diesel exports to
domestic uses. In addition to the approximately 560
million gallons imported into the U.S. in 2015, there
were about 90 million gallons exported from the United
States to overseas markets. One commenter used biodiesel import data from January 2012 through April
2016 to estimate that, based on the highest annual volume of biodiesel imports in the 55 cities that reported
biodiesel imports during this time period, the United
States current import capacity for biodiesel at these
cities is approximately 659 million gallons.141 Actual
import capacity is likely to exceed this volume, as this
estimate relied solely on historic import volumes, rather
than an assessment of the capacity of the infrastructure that could be used to import biodiesel at these 55
cities. It is also likely that under the right circumstances
141
See comments from Renewable Energy Group, Inc. (EPA–
HQ–OAR–2016–0004–3477). REG used data from the Energy
Information Agency in their assessment, and therefore did not capture renewable diesel imports. The total import capacity of biodiesel and renewable diesel therefore likely exceeds the volumes
estimated here.
275a
there are additional locations through which biodiesel
could be imported.
Given the right incentives, it may be possible to
increase net biodiesel and renewable diesel imports,
either by redirecting a portion of the biodiesel currently
consumed in foreign countries to be exported to the
U.S. and/or by reducing the volume of biodiesel exported from the United States. However, the amount of
biodiesel and renewable diesel that can be imported
into the United States is difficult to predict, as the
incentives to import biodiesel and renewable diesel to
the U.S. are a function not only of the RFS and other
U.S. policies and economic drivers, but also those in
the other countries around the world. These policies
and economic drivers are not fixed, and change on a
continuing basis. Over the years there has been significant variation in both the imports and exports of biodiesel and renewable diesel as a result of varying
policies and relative economic conditions (See Figure
V.B.2.iii–1 below). Increasing biodiesel and renewable
diesel imports significantly beyond the 659 million gallons estimated above would require a clear signal to the
parties involved that increasing imports will be economically advantageous and the potential re-negotiations
of existing contracts. It may also require upgrades and
expansions a U.S. import terminals. It is possible, but
uncertain, whether higher RFS standards could provide
such a signal. Also, to the degree that higher volumes
of imported biodiesel or renewable diesel to the United
States come at the expense of consumption in the rest of
the world, the environmental benefits of this increased
volume are expected to be modest.142 In this final rule
we have no projected biodiesel and renewable diesel
142
See Section IV.B.2 for a further discussion of this issue.
276a
imports separately from domestically produced biodiesel
and renewable diesel, since these fuels are subject to
the same potential limitation (e.g., feedstock availability, distribution and use constraints, etc.).143 We do
believe, however that the standards in this final rule
will result in an increase in biodiesel and renewable diesel imports consistent with the general trend observed
in previous years, and our projection of the supply of
these fuels in 2017 includes this expected increase.
Figure V.B.2.iii-1 1—
Biodiesel and Renewable Diesel
Imports and Exports (2012-2015)a
a
Import data reported through the EMTS system. Export data
sourced from EIA (http://www.eia.gov/dnav/pet/pet_move_expc_
a_EPOORDB_EEX_mbbl_a.htm)
143
As discussed in Section IV.B.2, we expect an increase of
approximately 100 million gallons of advanced biodiesel, advanced
renewable diesel, and/or feedstocks that can be used to produce
these fuels. We are also projecting an increase of 100 million gallons
of conventional biodiesel and renewable diesel. Historically the
majority of this fuel has been imported (see Table IV.B.2–2), and
we expect this will again be the case in 2017.
277a
iv. Biodiesel and Renewable Diesel Distribution Capacity
While biodiesel and renewable diesel are similar in
that they are both diesel fuel replacements produced
from the same types of feedstocks, there are significant
differences in their fuel properties that result in differences in the way the two fuels are distributed and consumed. Renewable diesel is a pure hydrocarbon fuel
that is nearly indistinguishable from petroleum-based
diesel. As a result, it can generally use the existing distribution infrastructure for petroleum diesel and there
are no significant constraints on its growth with respect
to distribution capacity. Biodiesel, in contrast, is an
oxygenated fuel rather than a pure hydrocarbon. It
historically has not been distributed through most
pipelines due to contamination concerns with jet fuel,
and may require specialized storage facilities, additives,
or blending with petroleum diesel to prevent the fuel
from gelling in cold temperatures. In the past few
years, however, a limited number of pipelines that do
not carry jet fuel have begun shipping biodiesel
blends.144 Recent changes to the ASTM jet fuel specifications allowing up to 50 ppm biodiesel,145 as well as
experience gained in isolating jet fuel from biodiesel in
pipelines may open new opportunities for distributing
biodiesel blends by pipeline in future years. A number
of studies have investigated the impacts of cold temperatures on storage, blending, distribution, and use of
144
See NBB comments on the Proposed Rule (EPA–HQ–OAR–
2016–0004–2904).
145
While the ASTM specification generally limits biodiesel
contamination in jet fuel to 50 ppm, up to 100 ppm biodiesel may
be allowed on an “emergency basis.” Subcommittee J intends to
consider a ballot to increase the limit of biodiesel in jet fuel to 100
ppm (See ASTM D1655).
278a
biodiesel, along with potential mitigation strategies.146
147 148
Information provided by the National Biodiesel
Board, as well as comments on our proposed rule, indicate that some retailers offer biodiesel blend levels that
differ in the summer and winter to account for these
cold temperature impacts.149 150 While cold temperatures can cause problems with the distribution and use
of biodiesel, the experiences of states such as Minnesota
and Illinois, where biodiesel is used year-round despite
cold winter weather, demonstrates that these challenges can be overcome with the proper handling of
biodiesel.151 152
The infrastructure needed to store and distribute biodiesel has generally been built in response to the local
demand for biodiesel. In some cases, the infrastructure
must be expanded to bring biodiesel to new markets
146
“Biodiesel Cloud Point and Cold Weather Issues,” NC State
University & A&T State University Cooperative Extension,
December 9, 2010.
147
“Biodiesel Cold Weather Blending Study,” Cold Flow Blending Consortium.
148
“Petroleum Diesel Fuel and Biodiesel Technical Cold
Weather Issues,” Minnesota Department of Agriculture, Report
to Legislature, February 15, 2009.
149
http://biodiesel.org/using-biodiesel/finding-biodiesel/re
tail-locations/biodiesel-retailer-listings.
150
See comment from CountryMark on the proposed rule (EPA–
HQ–OAR–2016–0004–1826).
151
Biodiesel is used year-round in Minnesota and Illinois in
large part due to state mandates and tax credits respectively, in
addition to the incentives provided by the RFS program.
152
“Report to the Legislature Annual Report on Biodiesel,”
Kevin Hennessy, Minnesota Department of Agriculture. January
15, 2016. Available online <https://www.leg.state.mn.us/docs/
2016/mandated/ 160162.pdf>.
279a
and additional infrastructure may also be needed to
increase the supply of biodiesel in markets where it is
already being sold. In other cases, sufficient infrastructure exists to increase the local supply of biodiesel and
biodiesel blends using existing infrastructure.
Another factor potentially constraining the supply of
biodiesel is the number of terminals and bulk plants
that currently distribute biodiesel. A study conducted
on behalf of the NBB used OPIS data to calculate that
biodiesel is currently offered at fuel terminals in 369
of the 563 cities (approximately 66%) that have terminals providing gasoline, diesel and/or biodiesel.153 In
addition to these terminals, biodiesel is often distributed from bulk plants or directly from biodiesel production facilities. At present, the Web site Biodiesel.org
lists over 600 distribution facilities reported as selling
biodiesel either in pure form or blended form, the majority of which are bulk plants.154 155 Biodiesel production
facilities also serve as important distribution centers
for biodiesel. According to a survey conducted by NBB,
30% of the biodiesel produced at facilities that responded
153
See Attachment 6 of the comments submitted by the
National Biodiesel Board (EPA–HQ–OAR–2016–0004–2904).
The report lists 453 cities with terminals that offer gasoline and
diesel, 369 that offer biodiesel or biodiesel blends, and 259 that
offer both petroleum diesel and biodiesel.
154
List of biodiesel distributers from Biodiesel.org Web site
(http://biodiesel.org/using-biodiesel/finding-biodiesel/locatedistributors-in-the-us/distributors-map). Accessed 10/8/15. This
list does not include terminals that distribute biodiesel or biodiesel blends.
155
Bulk plants are much smaller than major gasoline and
diesel distribution terminals, and generally receive diesel and
biodiesel shipped by trucks from major terminals.
280a
to the survey is sold directly to retailers.156 Direct sales
to retail stations provide a significant opportunity for
biodiesel producers to access local markets without
first transporting biodiesel to a terminal or bulk plant
for further distribution.
While there are a large number of biodiesel distribution points in the United States, including terminals,
bulk plants, and biodiesel production facilities, the
majority of these distribution points appear to be concentrated in the Midwest and most of the population
centers of the country. These same areas consume the
majority of the diesel fuel in the United States, and
thus have the greatest potential markets for biodiesel.
For the biodiesel market to continue to expand, it must
either increase the volume of biodiesel sold in markets
where it is already being sold, or expand into markets
that currently do not have access to biodiesel. Either
of these methods for expanding the biodiesel market
will likely require additional infrastructure. Transportation of the biodiesel from production facilities to retail
fuel stations, whether directly or through terminals
and bulk plants, will also need to be expanded for volumes to continue to grow. This will likely require additional trucks and/or rail cars,157 as biodiesel and biodiesel blends are currently generally not transported
in common carrier pipelines. If recent changes to the
ASTM specifications for jet fuel (discussed above) allow
156
See Attachment 6 of the comments submitted by the
National Biodiesel Board (EPA–HQ–OAR–2016–0004–2904).
157
Biodiesel can also be transported by barge, however we expect
that a limited number of biodiesel production facilities have access
to barge or ocean transportation. Survey data collected by NBB
indicates that only 7% of biodiesel is currently transported by
barge (see NBB comments on the proposed rule, attachment 6;
EPA–HQ–OAR–2016–0004–2904).
281a
for greater volumes of biodiesel blends to be shipped
by pipeline this would be a potentially significant
change, as it would likely allow for biodiesel distribution at terminals that currently do not have access to
biodiesel blends and could significantly reduce the cost
of distributing biodiesel. Distributing biodiesel via truck
or rail results in high fuel transportation costs (relative to petroleum derived diesel, which is generally delivered to terminals via pipelines), which may impact the
viability of adding biodiesel distribution capacity at a
number of existing terminals or bulk plants. It is likely
that until and unless significant volumes of biodiesel
blends are transported by pipeline, increasing the biodiesel market will require greater investment per volume of biodiesel supplied than in the past, as the new
biodiesel distribution facilities will generally have access
to smaller markets than the existing facilities, or will
face competition as they seek to expand into areas
already supplied by existing distribution facilities.
The net result is that the expansion of the distribution infrastructure required to transport biodiesel to
distribution points and retail stations and store it at
these locations will be necessary, whether biodiesel
consumption is increased through additional consumption in existing markets, expansion to new markets, or
some combination of the two. While this is not an insurmountable challenge, it will require time and investment, and may limit the potential for the rapid expansion of the biodiesel supply. In previous years the
expansion of biodiesel distribution and storage has
largely been enabled by high volume diesel retailers,
such as truck stops and travel centers. We believe this
is likely to be the case in the near future as well, however the rate of increase of biodiesel and renewable
diesel at these locations may slow as many are already
282a
supplying significant volumes of biodiesel and renewable diesel.
The distribution of biodiesel and biodiesel blends is
an area in which the biodiesel industry has made steady
progress over time, and we anticipate that this progress
can and will continue into the future, particularly with
the ongoing incentive for biodiesel growth provided by
the RFS standards. This is especially true to the
degree that excess biodiesel transportation infrastructure (trucks, rail cars, barges, etc.) and storage capacity currently exist. Low oil prices, however, may present
a challenge to the expansion of biodiesel distribution
infrastructure, since the profitability of such projects
in current market conditions is largely dependent on
government support such as the biodiesel blenders tax
credit and RFS RIN value.158 Since some investors
view such government supports as inherently uncertain
they may be hesitant to invest in new infrastructure
to enable additional biodiesel distribution at a time
when diesel prices are low. As with many of these potential supply constraints, increasing biodiesel storage
and distribution capacity will require time and investment, potentially limiting the potential growth in 2017
and future years.
v. Biodiesel and Renewable Diesel Retail
Infrastructure Capacity
For renewable diesel, we do not expect that refueling
infrastructure (e.g., refueling stations selling renewable
diesel blends) will be a significant limiting factor in
2017 due to its similarity to petroleum-based diesel and
the relatively small volumes expected to be supplied in
the United States. The situation is different, however,
158
See comments from NATSO (EPA–HQ–OAR–2016–0004–
1830).
283a
for biodiesel. Biodiesel is typically distributed to retail
stations in blended form with diesel fuel as blends
varying from B2 up to B20, and in some narrow cases
at levels exceeding B20. Biodiesel blends up to and
including B20 can be sold using existing retail infrastructure, and generally do not require any upgrades
or modifications at the retail level. Small retailers of
diesel fuel, however, generally have only a single storage
tank for diesel fuel, and can therefore generally only
offer a single biodiesel blend. We expect that many of
the retailers in this situation will be hesitant to offer
biodiesel blends above B5, as doing so would mean
only selling a fuel that is not recommended for use by
some vehicle and engine manufacturers (see following
section for a further discussion of potential engine warranty issues).
Large diesel fuel retailers, such as truck stops and
travel centers may have sufficient tankage to offer
multiple blends of diesel fuel and/or biodiesel, should
they choose to do so. Some of these large retailers have
biodiesel blending infrastructure at their retail facilities, allowing them greater control over the blends of
biodiesel sold at their stations. This is
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