Mandatory Reporting of Greenhouse Gases: Injection and Geologic Sequestration of Carbon Dioxide, 18576-18606 [2010-6766]
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Federal Register / Vol. 75, No. 69 / Monday, April 12, 2010 / Proposed Rules
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 98
[EPA–HQ–OAR–2009–0926; FRL–9131–2]
RIN 2060–AP88
Mandatory Reporting of Greenhouse
Gases: Injection and Geologic
Sequestration of Carbon Dioxide
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AGENCY: Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
SUMMARY: EPA is proposing a rule to
require reporting on carbon dioxide
(CO2) injection and geologic
sequestration (GS). The proposed
rulemaking does not require control of
greenhouse gases (GHGs), rather it
requires only monitoring and reporting
of CO2 injection and geologic
sequestration. EPA first proposed that
suppliers of CO2 be subject to
mandatory GHG reporting requirements
in April 2009 and finalized the rule for
suppliers of CO2 on October 30, 2009.
DATES: Comments. Comments must be
received on or before June 11, 2010.
Public hearings. There will be one
public hearing. The hearing date and
location is: April 19, 2010 from 9 a.m.
to 1 p.m. at One Potomac Yard, 2777 S.
Crystal Drive, Arlington, VA 22202.
To obtain information about the
public hearing or to register to speak at
the hearing, please go to https://www.
epa.gov/climatechange/emissions/
ghgrulemaking.html.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
OAR–2009–0926, by one of the
following methods:
Federal eRulemaking Portal: https://
www.regulations.gov. Follow the online
instructions for submitting comments.
E-mail: GHGReportingRR@epa.gov.
Fax: (202) 566–1741.
Mail: EPA Docket Center, Attention
Docket OAR–2009–0926, Mailcode
2822T, 1200 Pennsylvania Ave., NW.,
Washington, DC 20460.
Hand/Courier Delivery: EPA Docket
Center Public Reading Room, Room
3334, EPA West Building, Attention
Docket OAR–2009–0926, 1301
Constitution Ave., NW., Washington,
DC 20004. Such deliveries are only
accepted during the Docket’s normal
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hours of operation, and special
arrangements should be made for
deliveries of boxed information.
Instructions: Direct your comments to
Docket ID No. EPA–HQ–OAR–2009–
0926. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be confidential business
information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through https://
www.regulations.gov or e-mail. The
https://www.regulations.gov Web site is
an ‘‘anonymous access’’ system, which
means EPA will not know your identity
or contact information unless you
provide it in the body of your comment.
If you send an e-mail comment directly
to EPA without going through https://
www.regulations.gov your e-mail
address will be automatically captured
and included as part of the comment
that is placed in the public docket and
made available on the Internet. If you
submit an electronic comment, EPA
recommends that you include your
name and other contact information in
the body of your comment and with any
disk or CD–ROM you submit. If EPA
cannot read your comment due to
technical difficulties and cannot contact
you for clarification, EPA may not be
able to consider your comment.
Electronic files should avoid the use of
special characters, any form of
encryption, and be free of any defects or
viruses.
Docket: All documents in the docket
are listed in the https://
www.regulations.gov index. Although
listed in the index, some information is
not publicly available, e.g., CBI or other
information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
will be publicly available only in hard
copy. Publicly available docket
materials are available either
electronically in https://
www.regulations.gov or in hard copy at
EPA’s Docket Center, Public Reading
Room, EPA West Building, Room 3334,
1301 Constitution Ave., NW.,
Washington, DC. This Docket Facility is
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open from 8:30 a.m. to 4:30 p.m.,
Monday through Friday, excluding legal
holidays. The telephone number for the
Public Reading Room is (202) 566–1744,
and the telephone number for the Air
Docket is (202) 566–1742.
FOR FURTHER INFORMATION CONTACT: For
technical information, e-mail the
Greenhouse Gas Reporting Rule Hotline
at ghgmrr@epa.gov with the name of
this action in the e-mail subject line, or
contact Barbora Master, Climate Change
Division, Office of Atmospheric
Programs (MC–6207J), Environmental
Protection Agency, 1200 Pennsylvania
Ave., NW., Washington, DC 20460;
telephone number: (202) 343–9899; fax
number: (202) 343–2359. To obtain
information about the public hearings or
to register to speak at the hearings,
please go to https://www.epa.gov/
climatechange/emissions/
ghgrulemaking.html.
SUPPLEMENTARY INFORMATION:
Additional Information on Submitting
Comments: To expedite review of your
comments by Agency staff, you are
encouraged to send a separate copy of
your comments, in addition to the copy
you submit to the official docket, to
Carole Cook, Climate Change Division,
Office of Atmospheric Programs (MC–
6207J), Environmental Protection
Agency, 1200 Pennsylvania Ave., NW.,
Washington, DC 20460; e-mail address:
GHGReportingRule@epa.gov.
In drafting this proposed rulemaking,
EPA reviewed and considered
comments submitted on the proposed
subpart PP. However, as this is a new
proposal, EPA will not be responding to
comments received on the April 2009
proposed subpart PP in this rulemaking.
To ensure that their comments are
considered, stakeholders should submit
comments relevant to this rulemaking as
instructed in this document.
Regulated Entities. The Administrator
has determined that this action is
subject to the provisions of Clean Air
Act (CAA) section 307(d). See CAA
section 307(d)(1)(V) (the provisions of
CAA section 307(d) apply to ‘‘such other
actions as the Administrator may
determine’’). This is a proposed
regulation. If finalized, these regulations
would affect owners or operators of CO2
injection wells. Regulated categories
and entities include those listed in
Table 1 of this preamble:
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TABLE 1—EXAMPLES OF AFFECTED ENTITIES BY CATEGORY
Category
NAICS
Examples of affected facilities
CO2 Enhanced Oil and Gas Recovery Projects .........................
211
GS Sites ......................................................................................
N/A
Table 1 of this preamble is not
intended to be exhaustive, but rather
provides a guide for readers regarding
facilities likely to be affected by this
action. Table 1 of this preamble lists the
types of facilities that EPA is now aware
could be potentially affected by the
reporting requirements. Other types of
facilities not listed in the table could
also be subject to reporting
requirements. To determine whether
you are affected by this action, you
should carefully examine the
Oil and gas extraction projects using CO2 enhanced oil and
gas recovery.
CO2 geologic sequestration projects.
applicability criteria found in proposed
40 CFR part 98, subpart A or the
relevant criteria in the sections related
to the injection and GS of CO2. If you
have questions regarding the
applicability of this action to a
particular facility, consult the person
listed in the preceding FOR FURTHER
INFORMATION CONTACT section.
Some facilities that are affected by
today’s proposed rule have GHG
emissions from multiple source
categories. Table 2 of this preamble has
been developed as a guide to help
potential CO2 injection and GS reporters
subject to the proposed rule identify the
source categories (by subpart) that they
may need to (1) consider in their facility
applicability determination, and/or (2)
include in their reporting. The table
should only be seen as a guide.
Additional subparts in 40 CFR part 98
may be relevant for a given reporter.
Similarly, not all listed subparts are
relevant for all reporters.
TABLE 2—SOURCE CATEGORIES AND RELEVANT SUBPARTS
Source category
(and main applicable subpart)
Other subparts recommended for review to determine applicability
Injection and Geologic Sequestration of Carbon Dioxide ........................
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Acronyms and Abbreviations. The
following acronyms and abbreviations
are used in this document.
3–D three-dimensional
CAA Clean Air Act
CBI confidential business information
CCS carbon dioxide capture and geologic
sequestration
CDM Clean Development Mechanism
CFR Code of Federal Regulations
CH4 methane
CO2 carbon dioxide
DOE Department of Energy
EC European Commission
ECBM enhanced coalbed methane
EIA Economic Impact Analysis
EPA Environmental Protection Agency
EO Executive Order
ER enhanced oil and gas recovery
GHG greenhouse gas
GPG Good Practice Guidance
GS geologic sequestration
HFC hydrofluorocarbon
HFE hydrofluoroether
ICR Information Collection Request
IMO International Maritime Organization
IPCC Intergovernmental Panel on Climate
Change
IRS Internal Revenue Service
MRR Mandatory Reporting of Greenhouse
Gases Rule
MRV monitoring, reporting, and
verification
N2O nitrous oxide
NAICS North American Industry
Classification System
NTTAA National Technology Transfer and
Advancement Act
O&GJ Oil and Gas Journal
OAR Office of Air and Radiation
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40 CFR part 98, subpart C.
40 CFR part 98, subpart W (proposed).
40 CFR part 98, subpart PP.
OMB Office of Management and Budget
OW Office of Water
PFC perfluorocarbon
QA/QC quality assurance/quality control
R&D research and development
RFA Regulatory Flexibility Act
SBREFA Small Business Regulatory
Enforcement Fairness Act
SDWA Safe Drinking Water Act
SF6 sulfur hexafluoride
TSD technical support document
UIC Underground Injection Control
UNFCCC United Nations Framework
Convention on Climate Change
US United States
UMRA Unfunded Mandates Reform Act of
1995
USDA United States Department of
Agriculture
USDW underground source of drinking
water
VEF Vulnerability Evaluation Framework
Table of Contents
I. Background
A. Organization of This Preamble
B. Background on the Proposed Rule
C. Overview of the Proposal
D. Legal Authority
E. Relationship to the Proposed UIC Class
VI Rulemaking Under the Safe Drinking
Water Act
F. Relationship to Other CO2 Injection
Information Collection and Reporting
Efforts
II. Rationale for Reporting, Recordkeeping
and Verification Requirements
A. Definition of Reporting Facilities
B. Selection of Reporting Thresholds
C. Selection of Data To Be Reported
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D. Selection of Monitoring, Reporting, and
Verification (MRV) Plan Requirements
and Approval Process
E. Selection of Schedule and Process for
Reporting
F. Selection of Procedures for Estimating
Missing Data
G. Selection of Records to Retain
III. Economic Impacts of the Proposed Rule
A. How were compliance costs estimated?
B. What are the costs of the proposed rule?
C. What are the economic impacts of the
proposed rule?
D. What are the impacts of the proposed
rule on small businesses?
E. What are the benefits of the proposed
rule for society?
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act (RFA)
D. Unfunded Mandates Reform Act
(UMRA)
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act
J. Executive Order 12898: Federal Actions
to Address Environmental Justice in
Minority Populations and Low-Income
Populations
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I. Background
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A. Organization of This Preamble
This preamble is broken into several
large sections, as detailed in the Table
of Contents. The following paragraphs
describe the layout of the preamble and
provide a brief summary of each section.
Section I of this preamble contains the
basic background information about the
origin of this proposed rulemaking,
including a discussion of how it relates
to the finalized requirements for
Suppliers of CO2 (under 40 CFR, part
98, subpart PP) and to the Underground
Injection Control (UIC) program. This
section also discusses EPA’s legal
authority under the Clean Air Act (CAA)
to collect the proposed data, and the
benefits of collecting the data.
Section II of this preamble
summarizes the general provisions of
this proposed rulemaking for reporting
CO2 injection and GS. This section also
provides a brief summary of, and
rationale for, the selection of key design
elements. Specifically, this section
describes EPA’s rationale for the
proposed (i) definition of reporting
facilities, (ii) applicability thresholds,
(iii) data reporting requirements, (iv)
monitoring, reporting and verification
(MRV) plan requirements and process,
(v) schedule and process for reporting,
(vi) procedures for estimating missing
data, and (vii) recordkeeping
requirements. Thus, for example, there
is a specific discussion regarding
appropriate applicability thresholds,
monitoring methodologies and reporting
and recordkeeping requirements for all
CO2 injection facilities, and additional
requirements for facilities that conduct
GS. EPA describes the proposed options
for each design element as well as the
other options considered. Throughout
this discussion, EPA highlights specific
issues on which the Agency solicits
comment.
Section III of this preamble provides
the summary of the cost impacts,
economic impacts, and benefits of this
proposed rule from the Economic
Impact Analysis (EIA). Finally, Section
IV of this preamble discusses the
various statutory and executive order
requirements applicable to this
proposed rulemaking.
B. Background on the Proposed Rule
On December 26, 2007, President
Bush signed the fiscal year 2008
Consolidated Appropriations Act
authorizing funding for EPA to issue a
rule requiring the mandatory reporting
of greenhouse gas (GHG) emissions
(Consolidated Appropriations Act, 2008,
Pub. L. 110–161, 121 Stat. 1844, 2128
(2008)). An accompanying joint
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explanatory statement directed EPA to
‘‘use its existing authority under the
Clean Air Act’’ to develop a mandatory
GHG reporting rule.
The proposed Mandatory Reporting of
Greenhouse Gases Rule (MRR) was
signed on March 10, 2009, by
Administrator Lisa Jackson and was
published a month later (74 FR 16448,
April 10, 2009). After a 60-day comment
period, two public hearings, and
meeting with over 4,000 additional
people in over 150 groups via Webinars,
conferences, individual meetings, and
other forms of outreach, EPA issued a
final rule on October 30, 2009 (74 FR
56260). The MRR requires reporting of
GHG emissions and supply from all
sectors of the economy, including fossil
fuel suppliers, industrial gas suppliers,
and direct emitters of GHGs. The rule
does not require the control of GHGs;
rather the rule requires only that sources
above certain threshold levels monitor
and report those GHGs.
The final MRR covers the major GHGs
that are directly emitted by
anthropogenic activities. These include
carbon dioxide (CO2), methane (CH4),
nitrous oxide (N2O), hydrofluorocarbons
(HFCs), perfluorocarbons (PFCs), sulfur
hexafluoride (SF6), and other specified
fluorinated compounds (e.g.,
hydrofluoroethers (HFEs)) used in
boutique applications such as
electronics and anesthetics.1
The final rule contains 31 subparts,
each requiring reporting from a defined
source category. In order to meet the
reporting time, quality assurance, and
verification requirements of the rule,
EPA is establishing a facility-to-EPA
electronic reporting system to facilitate
collection of data under this rule. All
facilities that are covered under this rule
as reporters will use this data system to
submit required data.
Subpart PP requires the reporting of
CO2 supplied to the economy. Subpart
PP applies to all facilities with CO2
production wells, facilities with
production process units that capture
and supply CO2 for commercial
applications or that capture and
maintain custody of a CO2 stream to
sequester or otherwise inject it
underground, and to importers and
exporters of bulk CO2. During the public
comment period on the rule, EPA
received many comments on subpart PP
that CO2 injected underground should
be considered when estimating
1 These gases influence the climate system by
trapping in the atmosphere heat that would
otherwise escape to space. Additional information
about GHGs, climate change, climate science, and
other related issues, can be found at EPA’s climate
change Web site at https://www.epa.gov/
climatechange/.
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emissions from the CO2 supply
industry. Some commenters specified
that some of the CO2 supplied for the
purposes of enhanced oil and gas
recovery (ER) is additionally
sequestered rather than emitted and
characterized ER operations as ‘‘closed
systems’’ rather than emissive. Other
commenters stated that including
reporting requirements for geologically
sequestered CO2 would fill a critical gap
in the reporting system. EPA agrees that
ER is a potentially non-emissive end use
and that GS data reporting from ER sites
can assist EPA in quantifying the
amount of CO2 that is permanently and
securely geologically sequestered. In
addition, EPA agrees that GS reporting
requirements would provide
information and transparency on the
amount of CO2 injected and geologically
sequestered in the United States.
Although CCS is occurring now on a
relatively small scale, it could play a
larger role in mitigating GHG emissions
from a wide variety of stationary
sources. According to the Inventory of
U.S. Greenhouse Gas Emissions and
Sinks: 1990–2007, stationary sources
contributed 67 percent of the total CO2
emissions from fossil fuel combustion in
2007.2 These sources represent a wide
variety of sectors amenable to CO2
capture: electric power plants (existing
and new), natural gas processing
facilities, petroleum refineries, iron &
steel foundries, ethylene plants,
hydrogen production facilities,
ammonia refineries, ethanol production
facilities, ethylene oxide plants, and
cement kilns. Furthermore, 95 percent
of the 500 largest stationary sources are
within 50 miles of a candidate GS
reservoir.3 Estimated GS capacity in the
United States is over 3,500 Gigatons CO2
(GtCO2) (13,000 Gigatons CO2 at the
high end),4 although the actual capacity
may be lower once site-specific
technical and economic considerations
are addressed. Even if only a fraction of
that geologic capacity is used, CCS is
poised to play a sizeable role in
mitigating U.S. GHG emissions.
Many of the injection and monitoring
technologies that may be applicable for
2 U.S. EPA Draft Inventory of U.S. Greenhouse
Gas Emissions and Sinks, 1990–2007, Draft Report,
EPA 430–R–09–004. Available at: https://epa.gov/
climatechange/emissions/usinventoryreport.html.
3 Dooley, JJ, CL Davidson, RT Dahowski, MA
Wise, N Gupta, SH Kim, EL Malone. 2006. ‘‘Carbon
Dioxide Capture and Geologic Storage: A Key
Component of a Global Energy Technology Strategy
to Address Climate Change.’’ Joint Global Change
Research Institute, Battelle Pacific Northwest
Division. PNWD–3602.
4 DOE. 2008. Carbon Sequestration Atlas of the
United States and Canada (Atlas II). Available at:
https://www.netl.doe.gov/technologies/carbon_seq/
refshelf/atlasII/.
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GS are commercially available today
and will be more widely demonstrated
over the next 10 to 15 years.5 The oil
and natural gas industry in the United
States has over 35 years of experience of
injection and monitoring of CO2 in the
deep subsurface for the purposes of
enhancing oil and natural gas
production. This experience provides a
strong foundation for the injection and
monitoring technologies that will be
needed for commercial-scale CCS. U.S.
experience with ER combined with the
experience of four end-to-end
commercial CCS projects 6 and ongoing
research, demonstration, and
deployment programs throughout the
world, are building confidence that
geologic sequestration of large amounts
of CO2 can be achieved.
C. Overview of the Proposal
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Today, EPA is proposing to amend the
Mandatory Reporting of Greenhouse
Gases Program at 40 CFR part 98 to add
reporting requirements covering
facilities that conduct injection and
geologic sequestration of CO2.
EPA is proposing a tiered approach
for reporting requirements under this
subpart. The first tier of proposed
regulations would establish a set of
reporting requirements that would cover
all facilities that inject CO2
underground. As described in Section
II.C of this preamble, all facilities would
be required to report CO2 transferred
onsite from offsite sources, the source of
the CO2 (if known), and CO2 injected
underground.
The second tier of reporting
requirements would apply to GS
facilities. As described in Section II.C of
this preamble, GS facilities would be
required to calculate CO2 sequestered by
subtracting total CO2 emissions from the
CO2 injected in the reporting year. The
emitted quantity would include the
injected CO2 that leaked from the
subsurface to the surface (if any), CO2
produced with oil or natural gas where
ER operations are conducted at the GS
facility, fugitive or vented CO2
emissions from surface equipment, and
emissions from combustion sources
located within the facility boundary,
such as compressors.
5 Dooley, JJ, CL Davidson, RT Dahowski. 2009.
‘‘An Assessment of the Commercial Availability of
Carbon Dioxide Capture and Storage Technologies
as of June 2009.’’ Joint Global Change Research
Institute. Pacific Northwest National Laboratory.
PNNL–18520.
6 These projects are: Sleipner (Norwegian North
Sea)—1 Mt CO2/yr injected since 1996; Weyburn
(Canada)—1 Mt CO2/yr injected since 2000; In
Salah (Algeria)—1.2 Mt CO2/yr injected since 2004;
and Snohvite (Norwegian Barents Sea)—0.7 Mt
CO2/yr injected since 2008.
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EPA considered several options for
monitoring, reporting and verification
(MRV) of potential CO2 leakage 7 at GS
sites: do not require a MRV plan, require
a universal MRV plan that applies to all
GS sites, or require a site-specific MRV
plan. EPA is proposing to require
monitoring according to a site-specific
MRV plan, but is seeking comment on
all of the options considered. While the
risk of leakage at a well-selected and
well-managed GS site is expected to be
low, the Agency considers it important
for all facilities conducting GS to
demonstrate that they have met MRV
standards. The options described above
are discussed in more detail in Section
II.D of this preamble.
Data on CO2 injection and GS are
critical to informing CAA GHG policies.
This data would provide information
and transparency on the amount of CO2
injected and geologically sequestered in
the United States and, in combination
with other subparts of the MRR, would
enable EPA to track the flow of CO2
across a CCS system. In addition, this
information would enable EPA to
monitor the growth and efficacy of GS
(and therefore CCS) as a GHG mitigation
technology over time and to evaluate
relevant policy options. For example,
EPA would be able to track whether
incentives or regulations are needed to
encourage faster or further GS project
development. EPA would also be able to
track whether ER sites are reporting GS
and consider whether incentives or
regulations are needed. Where ER
facilities are reporting GS, EPA would
be able to evaluate ER as a potentially
non-emissive end use. In combination
with subpart PP, EPA would be able to
reconcile this data with CO2 supplied in
order to better understand the quantity
of CO2 supplied to emissive and nonemissive end uses. Furthermore, this
data would inform Agency policy
decisions under CAA sections 111 and
112 related to the use of CCS for
mitigating GHG emissions.
In developing this proposal, EPA
considered overlap between this
program and other programs. In July
2008, EPA proposed to amend its UIC
program to establish a new class of
injection well for GS projects (73 FR
43492 (July 25, 2008)). Today’s proposal
provides a pathway for CO2 injection
facilities to report to EPA as GS facilities
under the CAA, regardless of their UIC
permit classification. Under this
proposal, any facility sequestering CO2
underground can choose to qualify and
7 Leakage in this proposed rule is defined as the
movement of CO2 from the injection zone to the
surface (for example to the atmosphere, indoor air,
oceans or surface water).
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report as a GS facility for purposes of
this proposed rule.
Since subpart RR is an amendment to
the MRR, the general provisions of the
MRR (40 CFR part 98, subpart A) apply
to today’s proposed subpart RR unless a
provision is superseded by this subpart
that applies uniquely to facilities that
inject CO2 or that conduct GS. The
general provisions address the following
topics: The purpose and scope (40 CFR
98.1); who must report (40 CFR 98.2);
the general monitoring, reporting,
recordkeeping and verification
requirement (40 CFR 98.3); the
authorization and responsibilities of the
designated authority (40 CFR 98.4); how
a report is submitted (40 CFR 98.5);
definitions (40 CFR 98.6); the
standardized methods incorporated by
reference (40 CFR 98.7); the compliance
and enforcement provisions (40 CFR
98.8); and the mailing addresses (40
CFR 98.9).
Amendments to the General
Provisions. In a separate rulemaking,
package that was recently published
(March 16, 2010), EPA issued minor
harmonizing changes to the general
provisions for the GHG reporting rule
(40 CFR part 98, subpart A) to
accommodate the addition of source
categories not included in the 2009 final
rule (e.g., subparts proposed in April
2009 but not finalized in 2009, any new
subparts that may be proposed in the
future). The changes update 98.2(a) on
rule applicability and 98.3 regarding the
reporting schedule to accommodate any
additional subparts and the schedule for
their reporting obligations (e.g., source
categories finalized in 2010 would not
begin data collection until 2011 and
reporting in 2012).
In particular, we restructured 40 CFR
98.2(a) to move the lists of source
categories from the text into tables. A
table format improves clarity and
facilitates the addition of source
categories that were not included in
calendar year 2010 reporting and would
begin reporting in future years. A table,
versus list, approach allows other
sections of the rule to be updated
automatically when the table is
updated; a list approach requires
separate updates to the various list
references each time the list is changed.
In addition to reformatting the
98.2(a)(1)–(2) lists into tables, other
sections of subpart A were reworded to
refer to the source category tables
because the tables make it clear which
source categories are to be considered
for determining the applicability
threshold and reporting requirements
for calendar years 2010, 2011, and
future years.
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As part of today’s proposed rule, EPA
is proposing changes to subpart A to
accommodate subpart RR. Because all
CO2 injection and geologic sequestration
facilities (as defined in proposed 40 CFR
part 98, subpart RR) would be subject to
proposed subpart RR, EPA is proposing
that this source category be added to the
table of ‘‘all-in’’ source categories
referenced from 40 CFR 98.2(a)(1).8 For
facilities that become subject to the
MRR due to CO2 injection or geologic
sequestration, the first annual GHG
report would cover calendar year 2011
rather than 2010.
EPA is proposing to amend 40 CFR
98.2(a) so that the MRR applies to
facilities located on or under the Outer
Continental Shelf. These revisions are
necessary to ensure that any CO2
injection or GS facilities located on or
under the Outer Continental Shelf of the
United States would be required to
report. In addition, EPA is proposing
revisions to the definition of United
States to clarify that the United States
includes the territorial seas. Other
facilities located offshore of the United
States covered by the MRR program at
40 CFR part 98 would also be affected
by this change in the definition of
United States. For example, EPA is
proposing in a separate rule to revise the
MRR requirements to add a new
subpart, subpart W, to address
petroleum and natural gas systems. Any
comments specific to that issue should
be directed to the Agency in that
rulemaking, not this one. Finally, in
addition to the change to the definition
of United States, EPA is adding a
definition of ‘‘Outer Continental Shelf.’’
This definition is drawn from the
definition in the U.S. Code. Together,
these changes make clear that the MRR
applies to facilities on land, in the
territorial seas, or on or under the Outer
Continental Shelf of the United States,
and that otherwise meet the
applicability criteria of the MRR.
EPA also is proposing to amend 40
CFR 98.7 (incorporation by reference) to
include standard methods used in
proposed subpart RR.
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D. Legal Authority
EPA is proposing subpart RR under
the existing authority provided in CAA
section 114. As noted in the MRR, CAA
section 114 provides EPA with broad
authority to require information
mandated by this rule because such data
will inform and are relevant to EPA’s
carrying out a wide variety of CAA
8 Since we changed the list of covered
subcategories to tables, we are not providing
regulatory text in this proposal because the
preamble is clear.
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provisions (74 FR 66264). Under CAA
section 114(a)(1), the Administrator may
require emissions sources, persons
subject to the CAA, or persons whom
the Administrator believes may have
necessary information to monitor and
report emissions and provide such other
information as the Administrator
requests for the purposes of carrying out
the provisions in the CAA (except for a
provision of title II with respect to
motor vehicles).
As discussed in greater detail in the
response to comments for the final
MRR, the CAA provides EPA with broad
authority to require the comprehensive
and accurate information mandated in
this rule because such data will inform,
and are relevant to, EPA’s analyses of
various CAA provisions (Mandatory
Reporting of Greenhouse Gases, EPA’s
Response to Public Comment’s Section
3–Legal Issues). EPA may gather
information for a variety of purposes,
including for the purpose of assisting in
the development of implementation
plans or of emissions standards under
CAA section 111, determining
compliance with implementation plans
or such standards, or more broadly for
‘‘carrying out any provision’’ of the CAA.
In addition, CAA section 103 authorizes
EPA to establish a national research and
development program, including nonregulatory approaches and technologies
for the prevention and control of air
pollution as it relates to GHGs and
climate change.
The information from CO2 injection
and GS facilities will allow EPA to make
well-informed decisions about whether
and how to use the CAA to regulate
these facilities and encourage voluntary
reductions.
E. Relationship to the Proposed UIC
Class VI Rulemaking Under the Safe
Water Drinking Act
The Agency maintains a high-level of
coordination across EPA offices and
regions on GS activities and regulatory
development. EPA’s Office of Air and
Radiation (OAR) and Office of Water
(OW) work closely to promote safe and
effective implementation of GS
technologies while ensuring protection
of human health and the environment.
All Agency efforts related to GS,
including the UIC Class VI proposal
which is discussed in more detail
below, and this MRR proposal, are
closely coordinated.
EPA’s UIC program was established in
the 1970s to prevent endangerment of
underground sources of drinking water
(USDWs) from injection of various
fluids, including CO2 for ER, oil field
fluids, water stored for drinking water
supplies, and municipal and industrial
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waste. The UIC program, which is
authorized by Part C of the Safe
Drinking Water Act (SDWA) (42 U.S.C.
300h et seq.), is designed to prevent the
movement of such fluid into USDWs by
addressing the potential pathways
through which injected fluids can
migrate and potentially endanger
USDWs.
When EPA initially promulgated its
UIC program regulations, the Agency
defined five classes of injection wells at
40 CFR 144.6, based on similarities in
the fluids injected, construction,
injection depth, design, and operating
techniques. Wells injecting industrial
non-hazardous liquids, municipal
wastewaters or hazardous wastes
beneath the lowermost USDW are
categorized as Class I. Those injecting
fluids in connection with conventional
oil or natural gas production, enhanced
oil and gas production, and the storage
of hydrocarbons which are liquid at
standard temperature and pressure are
categorized as Class II. Class III wells
inject fluids associated with the
extraction of minerals, and those
categorized as Class IV inject hazardous
or radioactive wastes into or above
USDWs. Class IV injection wells are
banned unless authorized under an
approved Federal or State ground water
remediation project. Class V includes all
injection wells that are not included in
Classes I–IV. This well class provides
for Class V experimental technology
wells including those permitted as GS
pilot projects.9
In 2008, EPA proposed to amend the
UIC program to establish a new class of
injection well—Class VI—to cover the
underground injection of CO2 for the
purpose of GS, or long-term storage of
CO2 (73 FR 43492, July 25, 2008). The
proposed requirements would tailor
existing components of the UIC program
to address the unique nature of GS
projects so as to ensure that the
injection of large volumes of CO2 in a
variety of geologic formations for the
purposes of long term storage would not
endanger USDWs. The UIC Class VI
proposal does not require any facilities
to capture and/or sequester CO2; rather
the proposed requirements, if finalized,
would protect USDWs under the SDWA.
The SDWA does not provide authority
to develop regulations for all areas
related to GS such as capture or
transport. As outlined in the UIC Class
VI proposal, injection wells used for
injecting CO2 for the purposes of ER
would continue to be regulated and
permitted as Class II as long as any
9 See EPA UIC Guidance #83. Available at:
https://www.epa.gov/safewater/uic/
wells_sequestration.html.
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production is occurring. EPA received
significant comments on this proposed
approach and is currently evaluating
these comments for the final
rulemaking.
Facilities regulated under the UIC
program are required to collect and
report data, with minimum
requirements for the collection and
reporting of data established at the
Federal level. Where States are given
primacy over the UIC program, the data
collected under the UIC program varies.
Data currently collected under a Stateissued UIC permit is submitted to States
while, under today’s subpart RR
proposal, reporters will be submitting
data directly to EPA. The Agency
believes that State, local, and tribal
input is valuable in ensuring that the
subpart RR reporting requirements
appropriately build on the UIC program
requirements. EPA is seeking comment
on a number of topics and will look for
opportunities to conduct outreach with
State, local and tribal organizations
between proposal and finalization.
Today’s proposal builds on the UIC
program requirements for monitoring
with the additional goals of verifying
the amount of CO2 sequestered and
collecting data on CO2 surface emissions
from GS facilities. As described in
Section II.D of this preamble, EPA is
proposing that a facility’s UIC permit
may be used to demonstrate that certain
MRV plan requirements have been
fulfilled.
In the Agency’s August 2009 Notice of
Data Availability supplementing the
UIC Class VI proposal, EPA noted that
it was evaluating the need for a more
comprehensive regulatory framework
for GS. The Agency acknowledges that
regulatory clarity is essential for
enabling GS to move forward in a
manner that protects human health and
the environment. It is EPA’s intention to
coordinate GS requirements across
relevant statutory or other programs in
order to minimize any redundancies
and increase clarity for stakeholders.
The Agency seeks comment on whether
this is appropriate.
The proposed UIC Class VI rule is a
separate rulemaking action; the
comment period for that rulemaking
closed on December 24, 2008. EPA will
not be accepting or responding to
comments on the proposed UIC Class VI
rule through today’s proposal unless
related to a specific issue raised by this
action.
F. Relationship to Other CO2 Injection
Information Collection and Reporting
Efforts
In considering how to design this
proposal, EPA reviewed and took into
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account other domestic and
international reporting and monitoring
programs. Key programs are
summarized in this section.
The Department of Energy (DOE)
Energy Information Administration
implements a voluntary GHG reporting
program under section 1605(b) of the
Energy Policy Act of 1992, which
directed DOE to issue guidelines
establishing a voluntary greenhouse gas
reporting program (42 U.S.C. 13385(b)).
Under the Energy Information
Administration’s ‘‘1605(b) program,’’
reporters can choose to prepare an
entity-wide GHG inventory and identify
specific GHG reductions made by the
entity.10 Reporting tools were revised
and published in 2009 to assist entities
in preparing a preliminary estimate of
emissions. The 2007 updated 1605(b)
guidance outlines a voluntary process to
report data on CO2 sequestration.
Currently, no CO2 injection or
sequestration entity has reported under
the 1605(b) program per the 2007
guidelines. According to the Energy
Information Administration Web site,
the first reporting cycle under the
revised Voluntary Reporting of
Greenhouse Gases Program has not been
completed as of January 15, 2010. The
Energy Information Administration
anticipates issuing an annual report and
public use database for data reported
through 2008 by early 2010.11 The
1605(b) guidance requires the
implementation of a site-specific
monitoring plan, but this plan is not
evaluated by DOE to determine whether
the plan will provide for appropriate
monitoring. Four prescriptive
monitoring scenarios are offered with
grades ranging from ‘‘A’’ to ‘‘C’’, any of
which would be acceptable for
compliance with the 1605(b) program.
Furthermore, although the 1605(b)
guidance cites the importance of
reporting CO2 leakage should it occur,
the guidance does not include a
discussion of, procedures for, or
methodologies for using monitoring
technologies and techniques to quantify
the leakage. As a result of this, and the
fact that reporting is voluntary, the
1605(b) program would not meet the
data needs of this proposed rule.
The Internal Revenue Service (IRS)
made public IRS Notice 2009–83 Credit
10 Under the 1605(b) program an ‘‘entity’’ is
defined as ‘‘the whole or part of any business,
institution, organization or household that is
recognized as an entity under any U.S. Federal,
State or local law that applies to it; is located, at
least in part, in the U.S.; and whose operations
affect U.S. greenhouse gas emissions.’’ Available at:
https://www.pi.energy.gov/enhancingGHGregistry.
11 Available at: https://www.eia.doe.gov/oiaf/1605/
data_reports.html.
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for Carbon Dioxide Sequestration under
section 45Q on its Web site on October
8, 2009.12 The notice provides
procedures for the allocation of credits
for CO2 sequestration under section 45Q
of the Internal Revenue Code. Section
45Q was enacted by section 115 of the
Energy Improvement and Extension Act
of 2008, (October 3, 2008) and was
amended by section 1131 of the
American Recovery and Reinvestment
Act of 2009 (February 17, 2009). To
claim this credit, a taxpayer must follow
general monitoring and verification
principles, calculate CO2 sequestered in
the fiscal year using a mass-balance
equation, and report to IRS the amount
of qualified CO2 sequestered in the
fiscal year. Seventy-five million metric
tons of qualified CO2 can be taken into
account for this credit. The IRS
included a provision in the notice to
supersede its monitoring and
verification procedures and
requirements with procedures and
requirements finalized by EPA in future
GS rulemaking such as the UIC Class VI
proposal and this proposed rule.
EPA has concluded for a number of
reasons that the IRS data would not
meet the needs outlined in this
proposed rule. First, the IRS reporting
requirement will expire after 75 million
metric tons of CO2 is reported as
sequestered to IRS, at which point the
data collection will end. Second, the
level of reporting and transparency
would not meet the verification needs of
this proposed rule. GS facilities only
report the quantity of CO2 sequestered
to IRS. The data used to calculate
sequestration and the specific
monitoring procedures followed will
only be reviewed by IRS staff in the case
of an audit. Given the variability in
geology and other conditions at GS
facilities, EPA believes that the
monitoring approach at each GS facility
must be reviewed on a case-by-case
basis to ensure that it is appropriate for
the site-specific geologic and
operational conditions. Third, the IRS
does not outline procedures or provide
a mechanism for quantifying and
reporting any CO2 leakage that may
occur as is necessary for this proposed
rule.
EPA notes that the United States
submits an inventory of GHG emissions
that accounts for CCS to the Secretariat
of the United Nations Framework
Convention on Climate Change
(UNFCCC) each year. The UNFCCC,
ratified by the United States in 1992,
establishes an overall framework for
intergovernmental efforts to tackle the
12 Available at: https://www.irs.gov/irb/200944_IRB/ar11.html.
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challenge posed by climate change. The
United States has submitted the
Inventory of U.S. Greenhouse Gas
Emissions and Sinks (Inventory) to the
United Nations every year since 1993.
The annual Inventory is consistent with
national inventory data submitted by
other UNFCCC parties, and uses
internationally accepted methods for its
emission estimates. For more
information about the Inventory, please
refer to the following Web site: https://
www.epa.gov/climatechange/emissions/
usinventoryreport.htm.
The United States currently follows
the 1996 13 Intergovernmental Panel of
Climate Change (IPCC) guidelines in
preparing its Inventory, as
supplemented by IPCC Good Practice
Guidance (GPG) from 2000 14 and
2003 15. Since these guidelines do not
provide information on the accounting
of GS, EPA addressed CO2 usage in the
2007 Inventory by accepting some
general, top-down assumptions about
the end-use of supplied CO2. First, EPA
collected CO2 production data for
natural CO2 domes and estimated for
each dome the amount of CO2 used for
ER operations and the amount of CO2
used for non-ER operations. EPA
assumed that the percentage of naturally
produced CO2 used for non-ER
operations (e.g., food processing,
chemical production) was all emitted to
the atmosphere. The percentage used for
ER operations was assumed to be
sequestered. Second, EPA collected data
from industry on anthropogenic CO2
emitted from natural gas processing and
ammonia plants and accounted it as
emitted, regardless of whether the CO2
was captured or not.
The IPCC published new inventory
guidelines in 2006 16, which directly
address accounting for GS and include
methodologies for the estimation of
emissions from capture, transport,
injection, and GS of CO2. The guidelines
are based on the principle that the CCS
system should be accounted for in a
13 IPCC, 1996. ‘‘Revised 1996 IPCC Guidelines for
National Greenhouse Gas Inventories.’’ National
Greenhouse Gas Inventories Programme. Available:
https://www.ipcc-nggip.iges.or.jp/public/gl/
invs1.html.
14 IPCC. 2000. ‘‘Good Practice Guidance and
Uncertainty Management in National Greenhouse
Gas Inventories.’’ National Greehouse Gas
Inventories Programme. Available at: https://
www.ipcc-nggip.iges.or.jp/public/gp/english/.
15 IPCC. 2003. ‘‘Good Practice Guidance for Land
Use, Land-Use Change, and Forestry.’’ National
Greenhouse Gas Inventories Programme. Available
at: https://www.ipcc-nggip.iges.or.jp/public/
gpglulucf/gpglulucf.html.
16 2006 IPCC Guidelines for National Greenhouse
Gas Inventories: Volume 2—Energy. Chapter 5
Carbon Dioxide Transport, Injection, and Geological
Storage. Available at: https://www.ipccnggip.iges.or.jp/public/2006gl/index.htm.
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complete and consistent manner across
the entire Inventory. The approach
accounts for CO2 produced from natural
CO2 domes and captured at industrial
facilities as well as emissions from
capture, transport, and use. For GS
specifically, the IPCC guidelines outline
a Tier 3 methodology 17 for estimating
and reporting emissions based on sitespecific evaluations of each storage site.
EPA believes that the GS monitoring,
reporting, and verification requirements
of this proposed rule are consistent with
the 2006 IPCC guidelines.
In considering how to design this
proposal, EPA also took into account the
monitoring requirements adopted in
other countries, in particular other
UNFCCC member countries that have
already taken steps towards collecting
information for CCS to meet the 2006
IPCC guidelines. The Directive of the
European Parliament and of the Council
on the geological storage of carbon
dioxide (Commission decision 2007/
589/EC) establishes a legal framework
for the environmentally safe geological
storage of CO2. It requires European
Council (EC) member States to ensure
that each GS site operator will carry out
monitoring of the injection facilities, the
storage complex (including the CO2
plume), and, where appropriate, the
surrounding environment for detection
of any significant migration or leakage
of CO2 or any significant adverse effect
on the surrounding environment.
The directive requires that monitoring
frequency be determined by the
competent authority, and should be at
least once a year. A monitoring report
should be developed that describes the
quantities and properties of the CO2
streams delivered and injected,
including concentration of the CO2
streams, in the reporting period. The
parameters to be monitored include:
• Fugitive emissions of CO2 at the
injection facility;
• CO2 volumetric flow at injection
wellheads;
• CO2 pressure and temperature at
injection wellheads (to determine mass
flow);
• Chemical analysis of the injected
material; and
• Reservoir temperature and pressure
(to determine CO2 phase behavior and
state).
Per the directive, each GS site should
choose monitoring technology based on
best practices available at the time the
monitoring plan is designed. The
following options should be considered
and used when appropriate:
• Technologies that can detect the
presence, location, and migration paths
of CO2 in the subsurface and at the
surface;
• Technologies that provide
information about pressure-volume
behavior and aerial/vertical distribution
of CO2-plume to refine numerical 3–Dsimulation to the 3–D-geological models
of the storage formation; and
• Technologies that can provide a
wide aerial spread in order to capture
information on any previously
undetected potential leakage pathways
across the aerial dimensions of the
complete storage complex and beyond,
in the event of significant irregularities
or migration of CO2 out of the storage
complex.
In Australia, the Proposed
Greenhouse Gas Geological
Sequestration Regulations 2009 were
proposed to support the implementation
and administration of the Greenhouse
Gas Geological Sequestration Act 2008
and to address several CCS related
issues, including monitoring
requirements for GS. These regulations
require that each GS site develop a
monitoring and verification plan which
includes the following:
• Characteristics of the geological
formation into which the GHG
substance is to be injected and any
geological or other conditions that may
influence containment of a stored GHG;
• A description of the existing
environment above, on and below the
surface of the ground; and any resource
above, on and below the surface of the
ground that a person is entitled to
extract or use under a resource
authority;
• Details of the equipment proposed
to be used to monitor the behavior of
stored greenhouse gas substances, and
where it is to be located;
• Details of the techniques to be used
to monitor, the length of time that each
technique is to be used, and how often
each monitoring technique is to be
carried out; and
• The regulation also specifies that a
report on the outcome of all monitoring
and verification activities carried out
should be completed quarterly.
Other international efforts have also
been useful to EPA in developing the
requirements of this proposed rule. The
International Maritime Organization
(IMO) has published under the London
Protocol 18 two documents to provide
guidelines to parties for the assessment
of and implementation of disposal of
CO2 in sub-seabed geologic formations:
17 Tier 3 methods include either detailed
emission models or measurements and data at
individual plant level where appropriate.
18 Available at: https://www.imo.org/includes/blast
Data.asp/doc_id=10531/9%20%20CO2%20
Sequestration%20English.pdf.
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Specific Guidelines for Assessment of
Carbon Dioxide Streams for Disposal
into Sub-Seabed Geological Formations
(2009) and Risk Assessment and
Management Framework for CO2
Sequestration in Sub-Seabed Geological
Structures (2007). These guidelines
focus on several aspects of CCS
including:
• CO2 stream characterization
(chemical and physical properties);
• Waste prevention audit;
• Consideration of waste management
options;
• Action lists;
• Identification and characterization
of sub-seabed geological formation;
• Assessment of potential impacts;
• Monitoring and risk management;
and
• Permitting and permit condition.
Under the Kyoto Protocol, the Clean
Development Mechanism (CDM) is a
market-based mechanism that aids
countries in meeting their emission
limitation and reduction goals through
emission reduction (or removal) projects
in developing nations. These projects
allow companies in industrialized
countries to receive credits that can
either be put towards their emission
limitation or reduction, traded, or sold.
Two new proposed CDM methodologies
(NM0167 and NM0168) address CCS
activities.19 These new baseline and
monitoring methodologies have not yet
been approved by the CDM Executive
Board, but EPA continues to follow their
progress and to monitor for other GS
methodology proposals.
II. Rationale for Reporting,
Recordkeeping, and Verification
Requirements
A. Definition of Reporting Facilities
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1. CO2 Injection Facility
EPA is proposing that the CO2
injection facility be defined broadly to
cover wells or a group of wells that
inject CO2 into the subsurface or subseabed geologic formations. This
definition would encompass both
onshore and offshore facilities.
EPA is proposing a broad definition of
CO2 injection facility to ensure complete
reporting of basic information regarding
the CO2 transferred onsite, the source of
the CO2 if known, and the CO2 injected.
The broad definition also provides
reporters with flexibility either to report
this basic information on a well by well
basis or to group wells in an area for
reporting purposes. Given the proposed
threshold and applicability for CO2
injection facilities, a more specific
19 Available at: https://cdm.unfccc.int/about/ccs/
index.html.
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definition addressing the aggregation of
groups of wells in an area is not
necessary. As discussed in more detail
in Section II.B of this preamble,
however, EPA is soliciting comment on
the question of how to define the source
category if a more precise definition is
necessary.
2. GS Facility
EPA is proposing facilities injecting
CO2 for the long-term containment in
subsurface geologic formations would
meet the definition of GS in this
proposed rule and would report
additional information. EPA is
proposing that facilities that inject CO2
for ER would not be GS facilities unless
they inject CO2 for the long-term
containment in subsurface geologic
formations and submit and gain EPA
approval of an MRV plan.
To comply with the specific reporting
requirements discussed in Section II.C
of this preamble, the reporter would
need to identify the sources and surface
equipment making up the GS facility.
However, EPA recognizes that defining
the extent of a GS facility source may be
difficult. For example, there may be a
number of injection wells in an oilfield
under common ownership or common
control of which only a subset would be
considered GS facilities. In that
example, the question of whether and
how to aggregate various wells arises. In
addition, the CO2 plume and pressure
front associated with a GS facility may
extend for a distance beyond the
injection point, and widely separated
wells may be injecting into the same
pore space. Because EPA is seeking data
on the amount of CO2 sequestered by
these facilities and because EPA is
proposing an all-in threshold for these
facilities, EPA is proposing a narrow
definition of GS source to simplify the
reporting requirements associated with
emissions from combustion and surface
equipment. For purposes of this
reporting rule, EPA is proposing to
define a GS facility to include all
structures associated with the injection
of CO2 located between the points of
CO2 transfer onsite from offsite and the
injection well (or wells). A GS facility
that injects CO2 to enhance the recovery
of oil or natural gas will also include all
structures associated with production
located between the production wells
and the separators.
Although EPA is proposing a narrow
definition of GS facility, the proposed
rule would require GS facilities to
monitor over a spatial area that will
almost certainly extend beyond the
boundaries of the facility, as defined
here. Given that a main focus of this
proposal is to obtain information
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regarding the efficacy of GS, EPA
anticipates that the MRV plans for GS
facilities will need to require monitoring
over a broad area. This is discussed in
Section II.D of this preamble.
EPA seeks comment on its approach
to defining the boundary of the GS
facility. In particular, EPA seeks
comment on the question of whether
EPA should require the aggregation of
wells located in an area, and if so, what
rules should be applied for determining
what equipment comprises the source.
EPA seeks comment on whether the GS
facility should be defined to include the
spatial area of monitoring proposed in
Section II.D of this preamble. EPA also
seeks comment on whether it should
follow the approach for onshore
facilities in the proposed subpart W
regulations, which requires the
aggregation of equipment to the
geographic boundary of a single
hydrocarbon basin as defined by the
American Association of Petroleum
Geologists.
EPA is proposing to exempt research
and development (R&D) as defined at 40
CFR Part 98.6 from subpart RR,
consistent with the approach taken in
subparts C through QQ of the MRR. EPA
is also proposing that, for the purposes
of GS facility requirements under
subpart RR, research and development
means those projects receiving Federal
funding to research practices and
monitoring techniques that will enable
safe and effective long-term
containment of a gaseous, liquid, or
supercritical CO2 stream in subsurface
geologic formations. R&D projects
would not be required to submit an
MRV plan under subpart RR. EPA seeks
comment on how R&D projects are
defined and treated in this proposal.
3. Other CO2 End-Users
In developing this proposed rule, EPA
considered requiring reporting from
various other end-users of the CO2 that
is produced and supplied to the
economy, including both emissive and
potentially non-emissive applications.
EPA considered but is not proposing
requiring reporting from these other
end-users; EPA has concluded that
collecting information pursuant to
subpart PP on CO2 supplied to the
economy will provide EPA with the
necessary data on emissive volumes
while minimizing the number of
facilities impacted by this rule. EPA
seeks comment on this conclusion. The
Agency also seeks comment on whether
applications, such as precipitated
calcium carbonate and some cement
production, permanently sequester CO2
and if so, which industries this would
include; how many facilities operate in
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each of these industries; how much of
the CO2 consumed in each industry
would be sequestered; whether a
sequestration factor would be
reasonable in any case; and what
methodologies could be used to verify
this sequestration.
B. Selection of Reporting Thresholds
To determine the appropriate
threshold for reporting under subpart
RR, EPA considered both a threshold
based on the amount of CO2 emitted and
a threshold based on the amount of CO2
injected underground. EPA concluded
that an emissions-based threshold
would be problematic because of the
lack of data on the incidence and scale
of surface emissions and leakage from
injection and GS of facilities. EPA seeks
comment on how the Agency could
determine an emissions-based threshold
and detailed data underlying such an
approach. EPA accordingly analyzed
injection facilities based on the quantity
of CO2 injected underground and
considered whether an injection
threshold should apply. EPA evaluated
a no threshold option (i.e., all facilities
that inject CO2 would be required to
report), 1,000 metric tons per year,
10,000 metric tons per year, 25,000
metric tons per year, and 100,000 metric
tons per year per facility of CO2
injected.
To establish a count of CO2 injection
facilities, EPA relied on data reported in
the Oil and Gas Journal (O&GJ)
Enhanced Oil Recovery Survey
published in April 2008 (Volume 106,
Issue 15). EPA compiled all the projects
listed for miscible and immiscible CO2
floods 20 reported in the O&GJ survey. A
total of 105 active ER projects were
reported. In some cases multiple
projects were conducted by the same
company in an oil field. For the
purposes of this analysis, EPA grouped
these reported projects by field and by
owner or operator to align with typical
industry practices for reporting project
information to State oil and gas
commissions. This computation results
in eighty facilities for the facility count.
The O&GJ survey does not provide the
specific volume of CO2 used in each of
the active ER projects. To calculate the
estimated volume of CO2 injected at
each ER project, EPA took the total
amount of CO2 used daily for ER, as
reported by the U.S. EPA in the Draft
1990–2007 Inventory of U.S.
Greenhouse Gas Emissions and Sinks,21
apportioned it to each ER project
according to an average value for the
fractional production of oil attributed to
ER using CO2 as presented in the O&GJ
survey, and normalized the amount of
CO2 injection on an annual basis. EPA
recognizes that this is likely an
oversimplification of the actual
injection volumes used at each facility
and is seeking comment on whether it
is reasonable to rely on the principle
that higher production is a function of
higher CO2 injection volumes. If a
different analytical approach would be
more appropriate, EPA seeks detailed
recommendations on the alternative
approach as well as additional data that
would enable EPA to conduct a more
comprehensive analysis.
The results of the threshold analysis
are presented in Table 3 of this
preamble. For further information on
the assumptions underlying the
threshold analysis, please refer to the
general technical support document
(TSD) for this proposal.22
TABLE 3—CO2 INJECTION FACILITIES: EFFECT OF INJECTION THRESHOLD ON REPORTED AMOUNT OF CO2 INJECTED AND
NUMBER OF FACILITIES REQUIRED TO REPORT
All In .............................................................
1,000 ............................................................
10,000 ..........................................................
25,000 ..........................................................
100,000 ........................................................
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Reported amount of CO2 injected
Total estimated
national (metric
tons/yr of CO2
injected)
Threshold level (metric tons/yr of CO2
injected)
Total number of U.S.
facilities
40,111,639
40,111,639
40,111,639
40,111,639
40,111,639
80
80
80
80
80
Metric tons/yr of
CO2 injected
40,111,639
40,111,115
40,099,065
40,005,238
39,065,039
Percent
covered
100.0
100.0
100.0
100.0
97.4
Number of facilities
required to report
Number
80
74
71
65
48
Percent
covered
100.0
92.5
88.8
81.3
60.0
The analysis shown in Table 3 of this
preamble suggests that nearly all
injection data can be collected from
roughly half of operating facilities at an
injection threshold of 100,000 metric
tons/yr of CO2 injected. EPA considered
establishing an injection threshold of
100,000 metric tons/yr of CO2 injected.
However, a low CO2 injection or
production quantity in one year is not
a reliable prediction of the quantity that
may be injected in the following year or
in a year of full-scale operation. For
example, six of the eighty facilities
reported zero or near zero production
and therefore did not exceed the 1,000
metric tons threshold as shown in Table
3 of this preamble. However, these six
facilities may inject over this threshold
in the following year. In addition, more
than 40 of the 105 projects in this
analysis were described in the OG&J
survey as ‘‘just started’’ or pilot projects,
indicating that they may not be at fully
operational levels of CO2 injection.
Given the variability of CO2 injection
rates, EPA is proposing that all facilities
report irrespective of injection or
production quantities in the reporting
year.
EPA is proposing that all CO2
injection facilities would be required to
report the minimum information in
subpart RR (quantity of CO2 injected,
quantity of CO2 transferred onsite from
offsite, and source of the CO2 if known)
at no threshold. An all-in reporting
threshold would allow the Agency to
comprehensively track all CO2 supply
(as reported in Suppliers of CO2, subpart
PP) that is injected underground. This
approach is consistent with the all-in
requirements in the MRR for suppliers
of petroleum, natural gas, and coal-toliquid products (subparts LL, MM, and
NN), producers of industrial gases
(subpart OO), and suppliers of CO2
(subpart PP). It was reasonable to
require all of the facilities in these
source categories to report because it
would result in the most comprehensive
accounting possible, simplify the rule,
and permit facilities to quickly
determine whether or not they must
20 A miscible CO flood injects CO as a liquid at
2
2
high pressure to completely mix with oil and make
it flow more easily. An immiscible CO2 flood uses
lower pressures of CO2 to swell the oil and provide
additional gas pressure to move the oil.
21 U.S. EPA Draft Inventory of U.S. Greenhouse
Gas Emissions and Sinks, 1990–2007, Draft Report,
EPA 430–R–09–004. Available at: https://epa.gov/
climatechange/emissions/usinventoryreport.html.
22 Subpart RR General TSD (see docket ID No.
EPA–HQ–OAR–2009–0926).
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report; the same rationale applies for
this source category proposed today.
Furthermore, it would create a uniform
burden for all covered facilities,
ensuring a level playing field in, and
preventing fragmentation of, the ER
sector. EPA has estimated the cost for
CO2 injection facilities to comply with
the minimum reporting requirements in
this proposed rule and has determined
that the burden would be small, given
the equipment and data collection
efforts already in place at ER projects.
EPA seeks comment on whether an
all-in reporting threshold for injection
facilities is appropriate or if a 100,000
metric tons/yr of CO2 injected or other
threshold on quantity injected (e.g., 1
million metric tons/yr of CO2 injected)
should be applied, leveraging
information collected through the UIC
program. To apply a reporting threshold
to injection facilities, EPA would need
to more specifically define which wells
should be grouped together to delineate
an injection facility. One option would
be to group wells together by field as
EPA did with the OG&J data in this
threshold analysis. This definition
would not be appropriate for injection
facilities that are not producing oil or
gas, however, such as those injecting
into saline formations or coal seams. A
second option would be to group wells
together by basin. This definition would
not be appropriate for injection facilities
that are not producing oil or gas,
however, such as those injecting into
saline formations or coal seams. A third
option would be to group wells by UIC
permit; an injection well would be
delineated by individual well if
permitted by UIC as such and by a
group of wells if permitted by UIC as a
group. This definition would not be
appropriate for sub-seabed injection
wells outside the jurisdiction of SDWA.
A fourth option would be to define
injection facility as one individual well.
This definition could be impractical for
injection facilities that operate hundreds
of wells, however, such as some ER
projects. EPA seeks comment on which
of these options for delineating an
injection facility, or any options not
discussed, would be most appropriate in
the case that a reporting threshold based
on injection quantity is appropriate.
2. GS Facilities
Under this action, EPA is proposing
that the subset of CO2 injection facilities
that are conducting GS (i.e., a GS
facility) must report to EPA a second
tier of data. EPA considered whether a
threshold should apply to this second
tier of data given that it would place a
reporting burden on GS facilities.
However, EPA could not perform an
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analysis on GS facilities based on
emissions without data on actual or
expected GS facility emissions. EPA
also could not perform a threshold
analysis based on injection due to the
uncertainty around predictions of
injection quantities for potential GS
facilities. In addition, it is difficult to
predict how many injection facilities
would choose to report GS. Therefore,
EPA is proposing to exempt GS R&D
projects but otherwise require all GS
facilities to comply with the GS
monitoring, reporting, and verification
requirements of subpart RR, and that
they report fugitive, vented, and
combustion emissions from surface
equipment (under subpart W, RR, or C,
as applicable). An all-in threshold will
allow EPA to work with the earlymovers of this nascent industry and to
strengthen EPA’s understanding of GS.
EPA is seeking comment on the
proposed injection-based threshold
analysis approach and how the Agency
might use an alternative threshold
approach, such as an emissions-based
threshold or risk-based threshold. The
Agency is also seeking comment on
whether the threshold analysis
conducted for CO2 injection facilities
could also be applied to GS and, if so,
whether a 100,000 metric tons/yr of CO2
injected or other threshold (e.g., 1
million metric tons/yr of CO2 injected)
should be applied. The Agency requests
supporting data which could be used to
establish a threshold.
C. Selection of Data To Be Reported
This section describes the data that
injection facilities and GS facilities must
report under subpart RR. The first tier
of reporting requirements described is
for all facilities that inject CO2
underground. The second tier of
reporting requirements described is for
GS facilities only.
The first tier has three proposed
reporting requirements. First, EPA is
proposing that all CO2 injection
facilities report the mass of CO2
injected. This would be determined by
the mass flow or volumetric flow and
CO2 concentration of the CO2 stream
injected. Facilities must use mass flow
meters to accurately measure the mass
of the CO2 injected or volumetric flow
meters to accurately measure the
volumetric flow of the CO2 injected. To
minimize the purchase and installation
of new equipment, facilities subject to
the UIC program would be allowed to
measure the mass or volume of CO2
injected with the flow meters installed
for purposes of compliance with their
UIC permits. EPA accordingly is
proposing two methodologies for
making these calculations, depending
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on whether the facility is using a
volumetric or a mass flow meter. EPA is
proposing this approach so that
facilities can comply with these
reporting requirements regardless of the
type of flow meter already installed. In
the case of a facility using a volumetric
flow meter, EPA assumes that the
facility can determine operating
temperature and pressure, which would
allow for the volumetric flow of CO2 to
be converted from operating conditions
to standard conditions and, using a
density value for CO2 at standard
conditions and the measured
concentration of CO2 in the flow,
determine the mass of CO2. EPA seeks
comment on the assumption that
facilities can determine operating
temperature and pressure, and
alternative approaches for determining
the mass of CO2 using a volumetric flow
meter where operating temperature and
pressure cannot be determined.
Facilities would measure the CO2
concentration by sampling and testing
the injected stream at the flow meter.
With this approach, the flow and the
concentration would be measured at the
same point in the system for maximized
data accuracy. Accordingly, if the flow
meter were installed at the
compressor(s), then the concentration
would be measured at the
compressor(s). If the flow meter were
installed at the well(s), then the
concentration would be measured at the
well(s). EPA recognizes that a facility
with tens or hundreds of injection wells,
all of which have flow meters already
installed at the wellheads, may face a
significant burden in testing
concentration at each of those flow
meters. EPA seeks comment on
alternative locations other than the flow
meter(s) where concentration of the CO2
injected could be measured at decreased
burden without decreasing accuracy.
EPA also seeks comment on potential
methodologies to estimate concentration
of the flow injected if flow is measured
elsewhere, such as apportioning the
concentration of CO2 transferred onsite
and the concentration of recycled CO2 to
the quantities from each source.
Second, EPA is proposing that all CO2
injection facilities report the mass of the
flow transferred onsite from offsite to
verify the mass of CO2 reported as
injected. This would be determined by
the mass flow or volumetric flow and
CO2 concentration of the flow
transferred onsite from offsite. A subset
of CO2 injection facilities—facilities
conducting ER—inject a combination of
new CO2 transferred onsite from offsite
and old CO2 recycled from the
operation. Therefore, EPA would use
reported data on CO2 transferred onsite
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from offsite to estimate the amount of
CO2 recycled from ER operations.
EPA is proposing that all CO2
injection facilities monitor the CO2
concentrations and mass flow or
volumetric flow quarterly. The purpose
of these measurements is to account for
fluctuations in the CO2 concentration
over the reporting year. EPA seeks
comment on this proposal and on the
level of burden this frequency of
reporting requires for facilities following
different frequency parameters for their
UIC permit.
Third, EPA is proposing that all CO2
injection facilities would report the
source contracted to supply the CO2, if
known. EPA would seek information on
whether the CO2 was contracted from a
natural source (i.e., produced from a
natural CO2 dome) or an industrial
source. If an industrial source, EPA
would seek information on the type of
source if known (captured at a power
plant, pulp and paper mill, ethanol
plant, natural gas processing facility, or
other type of industrial source). This
would allow EPA to track the movement
of CO2 through a CCS system and any
shift toward anthropogenic CO2 supply
sources. Pipelines that carry CO2 to the
CO2 injection facility may contain a mix
of CO2 from various sources. EPA
recognizes that facilities may not know
the source of CO2 that they purchase.
Accordingly, EPA would require the
data to be reported only if known. EPA
seeks comment on the proposed
approach for reporting the source
contracted to supply the CO2 if known.
EPA recognizes that at this time the
source of CO2 injected underground is
predominantly CO2 produced from
natural CO2 domes. It is possible that GS
using naturally sourced CO2 may not
qualify as a GHG mitigation action
because the purpose of GS is to isolate
CO2 that would otherwise have been
emitted to the atmosphere. Under this
proposed rule, however, GS facilities
must report annual CO2 sequestered
regardless of the source.
EPA seeks comment on whether the
three reporting requirements described
above are sufficient or if there are
additional reporting requirements that
should apply to all CO2 injection
facilities. EPA is proposing that the best
available monitoring methods (BAMM)
provision outlined in § 98.3(d) of the
MRR would apply in 2011 to injection
facilities for the first tier of reporting
requirements. EPA seeks comment on
this proposal.
For this proposed rule, EPA also
considered, but is not proposing, that a
CO2 injection facility be required to
report only the CO2 injection data it
collects under its current UIC permit
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(under any class) or relevant permit in
the case of a facility that is outside
SDWA jurisdiction. Although this
would impose the lowest burden on the
reporter since no new data would need
to be collected, EPA would not receive
complete data on the mass of CO2
injected. While collection of injection
volume is a minimum monitoring
requirement for all UIC well classes,
CO2 concentration data are not.
Furthermore, facilities are not required
to report CO2 transferred onsite from
offsite sources or the source of CO2
under any UIC permit class.
EPA is proposing that GS facilities
would be required to report a second
tier of data in subpart RR. These
reporting requirements include the
amount of leakage of CO2 to the surface
(if any), the amount of CO2 in produced
oil or gas (for GS facilities conducting
active ER operations), the amount of
fugitive and vented CO2 emissions from
surface equipment, and the total annual
amount of CO2 sequestered using a mass
balance equation. In this equation, the
sum of the CO2 emissions listed above
would be subtracted from the amount of
CO2 injected to equal the amount of CO2
sequestered. These four reporting
requirements are described in more
detail below.
GS facilities must report CO2 leakage,
if any occurs from the subsurface
geologic formation to the surface. EPA is
not proposing specific procedures or
methodologies for detecting or
quantifying CO2 leakage. However, each
GS facility would be required to develop
and implement a site-specific approach
to monitoring, detecting, and
quantifying CO2 leakage based on five
requirements that are described in
Section II.D of this preamble.
Second, EPA is proposing that GS
facilities that are actively producing oil
or gas would be required to report the
quantity of CO2 produced out of the
subsurface with produced oil or natural
gas. This would be done by measuring
at each separator the volumetric flow or
mass flow and the concentration of a
CO2 stream. These GS facilities would
also report CO2 that remains in the oil
or gas after separation.
Third, unless already reported in the
petroleum and natural gas system
subpart, subpart W, EPA is proposing
that all GS facilities would be required
to report fugitive and vented CO2
emissions from surface components
located within the facility for which
procedures and methodologies are
provided in subpart W. This could
include pump blow-downs and fugitive
emissions from valves, flanges, and
compressors. EPA seeks these data to
better understand the volume of fugitive
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and vented GHG emissions at GS
facilities as compared to the volume of
CO2 sequestered. This information is an
important indicator of the effectiveness
of GS as a GHG mitigation technology.
In addition, fugitive and vented CO2
emissions will need to be included in
the mass balance calculation of GS if
they occur downstream of the CO2
injection flow meter or (if applicable for
ER projects) upstream of the production
flow meter. This is further discussed in
Section II.D.3 of this preamble. This
proposed rule does not impose a general
requirement for all CO2 injection
facilities to report fugitive and vented
CO2 emissions from surface components
since facilities that are not sequestering
CO2 would not report GS. EPA seeks
comment on this approach.
Lastly, EPA is proposing that GS
facilities use a mass balance equation to
calculate and report CO2 sequestered in
the subsurface geologic formation in the
reporting year. This reported data point
would be valuable for EPA as the
Agency tracks CO2 across a CCS system
and will provide EPA with information
on the performance of GS projects over
time. EPA seeks comment on this
approach.
Alternatively, EPA could approximate
CO2 sequestered in the subsurface
without proposing additional reporting
requirements for GS facilities, by using
data already reported on CO2 transferred
from offsite and CO2 injected. EPA
considered but did not propose this
approach because it does not account
for potential leakage from the subsurface
and does not properly account for CO2
fugitive or vented emissions from
surface equipment during postproduction, processing, transport, or
compression. Given the importance of
GS as a GHG mitigation technology,
EPA seeks to achieve an accurate
reporting of GS. EPA seeks comment on
the proposed requirements for GS
facilities.
EPA recommends that CO2 injection
and GS facilities review subparts C and
PP and proposed subpart W. Subpart C
provides GHG calculation procedures
and reporting requirements for
stationary fuel combustion devices that
combust solid, liquid, or gaseous fuel.
CO2 injection and GS facilities should
pay close attention to compressors and
pumps located within the facility
boundary. Subpart PP provides
procedures for calculating and reporting
quantities of CO2 supplied to the
economy. The subpart W proposal
covers petroleum and natural gas
systems by defining eight types of
facilities and providing calculation
procedures and reporting requirements
for the GHG emissions of specific
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equipment that may be located in those
facilities. CO2 injection and GS facilities
should review in particular the
definitions of onshore and offshore
petroleum and natural gas production
facilities.
EPA is proposing that if an injection
facility is not conducting GS, it would
determine applicability to other
subparts of the rule separately from
applicability to subpart RR (see Table 4
of this preamble). This is similar to the
approach taken by reporters of upstream
petroleum products supply, natural gas
supply, natural gas liquids supply, and
carbon dioxide supply (reporters in
subparts MM, NN, and PP). For
example, an injection facility not
characterized as a GS facility would not
automatically trigger reporting under
subpart C by this proposal, but would
make a separate applicability
determination under subpart C. A GS
facility would automatically trigger
applicability under other subparts of the
rule. This is similar to the approach
taken by reporters of downstream
emissions in the rest of the MRR. For
example, the GS facility would report
under subpart C the emissions from
combustion sources located within the
facility boundary, such as compressors.
TABLE 4—REPORTING REQUIREMENTS IN MRR FOR CO2 INJECTION AND GS FACILITIES (IN SUBPART RR, SUBPART C,
AND PROPOSED SUBPART W)
Injection facilities (no GS)
GS facilities
Data to report
ER
Quantity of CO2 transferred
onsite.
Source of CO2 if known ........
Quantity of CO2 injected .......
Fugitive and vented CO2
emissions from surface
equipment.
Emissions from combustion
sources.
Quantity of CO2 produced
with oil or natural gas.
Percent of CO2 estimated to
remain with the oil and gas.
Quantity of CO2 emitted from
the subsurface.
Quantity of CO2 sequestered
Other
With ER
Other
subpart RR ...........................
subpart RR ...........................
subpart RR ...........................
subpart RR.
subpart RR ...........................
subpart RR ...........................
subpart W .............................
subpart RR ...........................
subpart RR ...........................
Not Applicable ......................
subpart RR ...........................
subpart RR ...........................
subpart W or subpart RR 1 ...
subpart RR.
subpart RR.
subpart RR.
Separate applicability determination.
Not Required ........................
Separate applicability determination.
Not Required ........................
subpart C 2 ............................
subpart C 2.
subpart RR ...........................
subpart RR.
Not required ..........................
Not required ..........................
subpart RR ...........................
Not applicable.
Not Required ........................
Not Required ........................
subpart RR ...........................
subpart RR.
Not Applicable ......................
Not Applicable ......................
subpart RR ...........................
subpart RR.
1 Subpart
2 All
W if the facility meets the subpart W threshold; if not then report in subpart RR.
GS facilities will be required to report combustion emissions according to subpart C.
In selecting data to be reported under
today’s proposal, EPA compared
reporting requirements under today’s
subpart RR proposal with reporting
under the UIC Class VI proposal (see
Table 5 of this preamble). EPA found
two data elements with potential
overlap. The first area of potential
overlap is the reporting of the amount
(flow rate) of injected CO2. The UIC
Class VI and subpart RR proposals differ
in the measurement unit and collection/
reporting frequency. EPA determined
that reporting of the amount (flow rate)
of injected CO2 was necessary in order
to harmonize the data with other
subparts of the MRR. To ensure that
data needs are harmonized between the
MRR and the UIC program requirements
and to reduce burden, and because this
data under a State-issued UIC permit is
currently submitted to States while,
under today’s subpart RR proposal,
reporters will be submitting data
directly to EPA. EPA will look for ways
to integrate data management between
the UIC and MRR programs and the
Agency is seeking comment on
reporting the amount (flow rate) of CO2
injected for purposes of this proposal.
TABLE 5—DATA ELEMENTS REPORTED UNDER UIC CLASS VI PROPOSAL AND SUBPART RR PROPOSAL
Subpart RR proposal
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Data element
UIC class VI proposal
Quantity of CO2 transferred onsite ..................................
Quantity (flow rate) of CO2 injected ................................
Fugitive and vented emissions from surface equipment
Quantity of CO2 produced with oil or natural gas (ER) ..
Percent of CO2 estimated to remain with the oil and gas
(ER).
Quantity of CO2 emitted from the subsurface .................
Quantity of CO2 sequestered in the subsurface .............
Cumulative mass of CO2 sequestered in the subsurface
Monitoring plan ................................................................
The second area of potential overlap
relates to monitoring plans. Although
both the UIC Class VI proposal and
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CO2 injection facilities (no
GS)
No ......................................
Yes ....................................
No ......................................
No ......................................
No ......................................
Yes ....................................
Yes ....................................
No ......................................
No ......................................
No ......................................
Yes.
Yes.
Yes.
Yes.
Yes.
No ......................................
No ......................................
No ......................................
Yes ....................................
No
No
No
No
Yes.
Yes.
Yes.
Yes.
......................................
......................................
......................................
......................................
today’s subpart RR proposal have
monitoring plan requirements, the UIC
Class VI proposal is focused on
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protection of USDWs, while today’s
subpart RR proposal is focused on air
emissions. Potential differences include
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baseline data and detection and
measurement of CO2 leakage to the
surface. Recognizing that air monitoring
under the UIC Class VI proposal is at the
discretion of the UIC director, EPA
notes that a UIC Class VI permit may
fulfill requirements under today’s
proposal.
EPA considered whether a GS facility
should also report methane (CH4)
leakage emissions from the subsurface.
CH4 emissions from the subsurface may
occur at oil and natural gas reservoirs or
ECBM sites. The cases in which leakage
of CH4 could occur at these sites may be
similar to the potential for CO2 leakage.
CH4 leakage could potentially occur
through improperly sealed wells, open
faults, and other pathways that have
also been identified as potential CO2
leakage pathways. However, CH4 is
present as a gas, and thus may be more
upwardly mobile than CO2 which is
injected as a supercritical fluid.
Therefore, the potential for leakage of
methane at depleted oil and gas or
ECBM sites may be greater than for CO2.
EPA is proposing to focus on CO2
emissions. EPA recognizes the potential
for CH4 leakage from the subsurface at
facilities conducting GS in oil and gas
reservoirs or coal seams and therefore
seeks comment on whether to require
reporting on CH4 leakage. If the
potential for CH4 leakage exists, the GS
reporter could include in the MRV plan
a monitoring strategy to detect and
quantify potential CH4 leakage. CH4
fugitive and vented emissions from
surface equipment are covered under
the proposed oil and gas subpart,
subpart W.
Under subparts C through QQ of the
MRR, adjacent or contiguous equipment
in actual physical contact under
common ownership or common control
constitute a facility (see Section 98.6 of
the MRR). In the case of petroleum and
natural gas systems and GS, equipment
are not necessarily in physical contact
with one another in the conventional
sense of the term. Subparts W and RR
are each proposing interpretations of
what would constitute a facility. As a
result, a GS facility conducting ER may
apply one facility boundary for
reporting under subpart W and a
different facility boundary for reporting
under subpart RR. EPA acknowledges
that this may present a challenge for
submitting annual reports, depending
on how the data system is designed. A
CO2 injection or GS operation would
submit an annual report to EPA
according to the proposed definition of
facility discussed in Section II.A of this
preamble. EPA seeks comment on a
resolution that would reduce reporting
burden while still meeting the data
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needs of both proposed subparts W and
RR.
EPA also recognizes that, in the case
of an ER operation conducting GS, the
combustion emissions from equipment
within the GS facility would be
included in both annual reports.
Though this approach results in
duplicative reporting, EPA has
concluded that to analyze the efficacy of
GS as a GHG mitigation tool, EPA needs
to collect information on combustion
emissions from GS facility equipment at
only the GS facility level rather than
aggregated with emissions from
additional equipment. EPA seeks
comment on this approach for reporting
combustion emissions from GS
facilities.
D. Selection of Monitoring, Reporting,
and Verification (MRV) Plan
Requirements and Approval Process
1. Selection of MRV Plan Option
EPA considered three alternatives for
monitoring, reporting and verification of
potential CO2 leakage at GS sites: do not
require an MRV plan, require a
universal MRV plan that applies to all
GS sites, or require a site-specific MRV
plan. The three alternatives vary in
stringency and specificity as described
below. EPA outlines the advantages and
disadvantages of each alternative and
seeks comment on each alternative, as
well as any alternatives not discussed.
Under the first alternative, EPA would
allow GS facilities to report the amount
of CO2 sequestered without requiring an
MRV plan. Under this alternative, the
Agency would rely on published
information and existing studies to
assume that injected CO2 remains
sequestered and would assume these
results can be generalized to all GS
projects. This alternative would impose
the least burden on reporters. EPA notes
that international guidelines on
information collection and reporting
efforts outlined in Section I.E of this
preamble do not support this approach.
Furthermore, EPA did not propose this
approach because of the limited
empirical data and the variability in
geology and other conditions among GS
facilities.
The second alternative that EPA
considered was a one-size-fits-all MRV
plan approach under which the Agency
would prescribe specific monitoring
technologies and quantification
methods for GS facilities. The advantage
of this approach is that all GS facilities
would use the same monitoring
technologies and methods. The
disadvantage of this approach is that the
geology and other conditions at
potential GS facilities will vary from site
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to site and a one-size-fits all approach
may not provide the most effective
monitoring strategy for all facilities.
EPA notes that international guidelines
on information collection and reporting
efforts outlined in Section I.E of this
preamble do not support this approach.
In addition, since the monitoring and
testing plans implemented under the
UIC program are necessarily sitespecific in nature, it would be difficult
to prescribe a one-size-fits-all MRV plan
that would complement and build upon
the UIC program. This alternative would
likely be the least cost effective and
most burdensome approach for
reporters.
The third alternative, and the
alternative that EPA is proposing, is that
GS facilities be required to develop a
site-specific MRV plan and submit it to
EPA for approval. Facilities would
report CO2 injection until the final MRV
plan has been approved. Once a final
MRV plan has been approved by EPA,
GS facilities would implement the plan,
including the reporting of the amount of
CO2 that has been sequestered. The
advantage of this approach is that it
provides a flexible and cost-effective
option for reporters and complements
monitoring requirements under the
proposed UIC Class VI rule. EPA
recognizes that the rigorous proposed
UIC Class VI requirements will provide
the foundation for the safe sequestration
of CO2 and should serve to reduce the
risk of CO2 leakage to the atmosphere
when finalized. An adequate MRV plan
would be tailored to site-specific
conditions and be designed for each
stage of the GS project. In addition, the
MRV plan would allow for modification
or adaptation of the plan based on
monitoring results. Although the risk of
leakage at an appropriately selected and
managed GS facility may be low, the
MRV plan would ensure that if leakage
occurs, the GS reporter would have an
approved methodology for measuring
the emitted CO2. If leakage occurs, the
MRV plan would also provide a process
for revising the MRV plan, if necessary,
as described in section II.E of this
preamble.
It is important to recognize that this
proposed rule is a data collection and
monitoring proposal which does not
directly address the potential human
health and welfare, ground or surface
water, ecosystem or geosphere impacts
of GS. Therefore, the proposed rule does
not address these potential impacts from
CO2 leakage (e.g., requiring remediation
or mitigation) as this is outside the
scope of this proposal.
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2. Background on MRV Approaches
EPA has identified published studies
and/or guidelines on monitoring
programs that identify and quantify CO2
leakage from GS facilities.23 While the
science of quantifying CO2 leakage from
GS facilities is evolving, it is generally
recognized that, when properly planned
and implemented, monitoring methods
will be effective at detecting
leakages.24, 25
Though the methodologies for
detecting and quantifying leakage of
CO2 from GS facilities have not been
standardized, EPA has concluded that a
GS facility would be able to propose a
site-specific plan for leak detection and
quantification under this rule based on
the current availability of monitoring
technologies. A wide range of
techniques for monitoring sequestration
of CO2 have been used for a number of
years in other applications, including
oil and natural gas production, natural
gas storage, disposal of liquid and
hazardous waste in deep geologic
formations, groundwater monitoring,
and ecosystem research.26 Some
monitoring techniques such as seismic
monitoring can detect the presence and
location of CO2 in the subsurface,
including both vertical and lateral
spread, although the accuracy of seismic
monitoring for quantifying the amount
of CO2 may be more limited than other
approaches. Other techniques, such as
soil gas monitors or eddy covariance
techniques, can detect, within a certain
limit, leakage of CO2 from the confining
system. Many of these technologies have
excellent sensitivity, and have been
shown to be able to detect relatively low
concentrations of CO2 above background
levels. The minimum leakage rate
detectable is a function of parameters
such as the volume of CO2 making its
way to the surface, the size of the leak
area, and the sensitivity of the
monitoring device.
Descriptions of the various
monitoring technologies that could be
deployed at a GS facility can be found
in the general TSD to this proposal.27
EPA seeks comment on the general TSD
3. MRV Plan Requirements
EPA is proposing that each submitted
MRV plan must include at a minimum
the four requirements described below:
• Step 1—Assessment of Risk of
Leakage: All potential pathways that
may result in CO2 leakage have been
identified and characterized and the risk
of CO2 leakage at each pathway has been
evaluated;
• Step 2—Strategy for Detecting and
Quantifying CO2 Leakage to Surface:
Potential pathways will be monitored
according to the risk of CO2 leakage to
ensure that any leakage to the surface
will be detected and that leakage to the
surface, should it occur, will be
quantified according to a specified
methodology;
• Step 3—Strategy for Establishing
Pre-Injection Environmental Baselines:
Environmental baselines against which
the monitoring results will be evaluated
have been established at potential
leakage pathways; and
• Step 4—Tailor Mass Balance
Equation: Site-specific variables have
been considered and developed for the
mass balance equation provided in the
regulatory text to calculate the amount
of CO2 sequestered.
These requirements are consistent
with the IPCC Guidelines for National
Greenhouse Gas Inventories (2006), as
well as the other information collection
and reporting efforts outlined in Section
I.F of this preamble.
EPA developed a monitoring plan
TSD that describes characteristics of a
robust monitoring plan, and provides
descriptions of potential GS geologic
settings, potential leakage pathways,
and the goals of monitoring.28 The
monitoring plan TSD uses EPA’s
Vulnerability Evaluation Framework
(VEF) to describe potential
vulnerabilities that may influence the
risk for CO2 leakage from a GS project
and is not intended to be used as a step
by step guide to develop an MRV plan.
The VEF includes a holistic discussion
of the potential impacts of GS. The VEF
is also provided in the docket.29 EPA
seeks comment on the monitoring plan
TSD.
In developing the proposed MRV plan
requirements, EPA compared
monitoring requirements under the UIC
Class VI proposal with those under
today’s MRR proposal, as shown in
Table 6 of this preamble. Monitoring
requirements under the UIC Class VI
proposal are focused on demonstrating
that USDWs are not endangered as a
result of CO2 injection into the
subsurface. As proposed, a UIC Class VI
permit would require a site
characterization and assessment of
leakage pathways for the purpose of
protection of USDWs. Therefore, EPA is
proposing that a UIC Class VI permit
may be used to demonstrate to EPA that
the assessment of risk of leakage step of
the MRV plan has been satisfied. The
UIC Class VI proposal indicates that UIC
Class VI permits may include surface
monitoring at the UIC Director’s
discretion. To the extent that the UIC
Class VI permit includes these surface
monitoring and related environmental
baseline components, it may be used to
demonstrate to EPA that the strategy for
detection and measurement of leakage
to the surface and the strategy for
establishing pre-injection environmental
baselines have been satisfied. EPA seeks
comment on allowing the use of a UIC
Class VI permit to fulfill certain MRV
plan requirements, whether there are
situations where EPA’s proposal to rely
on a UIC Class VI permit would not be
sufficient.
23 Arts, R, O Eiken, A Chadwick, P Zweigel, L van
der Meer, B Zinszner. 2004. ‘‘Monitoring of CO2
injected at Sleipner using time-lapse seismic data.’’
Energy 29: 1383–1392; Wilson, M. and M. Monea
(Eds.). 2004. ‘‘IEA GHG Weyburn CO2 Monitoring
and Storage Project,’’ Seventh International
Conference on Greenhouse Gas Control
Technologies, Vol. 3; Klusman, RW. 2003. ‘‘Rate
Measurements and Detection of Gas Microseepage
to the Atmosphere from an Enhanced Recovery
Sequestration Project, Rangely, Colorado, USA,’’
Applied Geochemistry, 18, 1825–1838; 2006 IPCC
Guidelines for National Greenhouse Gas
Inventories: Volume 2—Energy. Chapter 5 Carbon
Dioxide Transport, Injection, and Geological
Storage. Available at: https://www.ipccnggip.iges.or.jp/public/2006gl/index.htm.; DOE/
NETL. 2009. ‘‘Best Practices for Monitoring,
Verification, and Accounting for CO2 Stored in
Deep Geologic Formations.’’ U.S. Department of
Energy, National Energy Technology Laboratory.
24 Benson, SM. 2006. ‘‘Monitoring Carbon Dioxide
Sequestration in Deep Geological Formations for
Inventory Verification and Carbon Credits.’’ Society
of Petroleum Engineers Paper 102833.
25 FutureGen Alliance. 2006. ‘‘Mattoon Site
Environmental Information Volume.’’ December
2006.
26 Benson, S and L Myer. 2002. ‘‘Monitoring to
Ensure Safe and Effective Geological Sequestration
of Carbon Dioxide.’’ Lawrence Berkeley Laboratory,
Berkeley, California; Benson, SM. 2002. ‘‘Geologic
Sequestration of Carbon Dioxide.’’ The Carbon
Dioxide Dilemma, Promising Technologies and
Policies, Proceedings of a Symposium, National
Academy of Engineering, April 23–24, 2002,
Washington, DC, pp. 29–39.
27 Subpart RR General TSD (see docket ID No.
EPA–HQ–OAR–2009–0926).
28 Monitoring Plans for Geologic Sequestration
TSD (see docket ID No. EPA–HQ–OAR–2009–0926).
29 Vulnerability Evaluation Framework for
Geologic Sequestration of Carbon Dioxide (see
docket ID No. EPA–HQ–OAR–2009–0926).
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and seeks additional data and
information on monitoring technologies
for leak detection and quantification.
Additional information on GS
monitoring technologies can also be
found in the IPCC Guidelines for
National Greenhouse Gas Inventories
(2006), the API/IPECA Inventory
Guidelines for CCS (2007), Department
of Energy MVA Best Practices Manual
(2009), and the International Energy
Agency GHG R&D Programme
monitoring tool Web site
(www.co2captureandstorage.info/
co2monitoringtool).
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TABLE 6—PROPOSED MRV PLAN ELEMENTS UNDER UIC CLASS VI PROPOSAL AND SUBPART RR PROPOSAL
Proposed MRV plan element
Required under UIC Class VI
proposal
Assessment of Risk of Leakage .............................................................
Strategy for Detecting and Quantifying CO2 Leakage to Surface ..........
Strategy for Establishing Pre-Injection Environmental Baselines at Surface.
Tailor Mass Balance Equation ................................................................
to USDWs ......................................
No ..................................................
No ..................................................
to surface.
Yes.
Yes.
No ..................................................
Yes.
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Reporters that do not hold UIC Class
VI permits would be required to provide
the MRV plan element information
outlined in this section.
Assessment of Risk of Leakage to the
Surface. EPA is proposing that the GS
facility reporter must provide sufficient
information in the MRV plan to
demonstrate to EPA that the potential
risk for CO2 leakage to the surface has
been evaluated. This evidence must be
‘‘a combination of site characterization
and realistic models that predict the
movement of CO2 over time and
locations where emissions might
occur’’.30 EPA seeks this information to
evaluate the leak detection strategy put
forth by the reporter in the MRV plan.
EPA believes this information is
reasonable to request because it
determines the boundaries of the area
which will be monitored for potential
CO2 leakage. The risk assessment for
CO2 leakage allows the reporter to target
monitoring in specific areas within
these boundaries.
EPA is proposing that to demonstrate
to the Agency that the risk of leakage to
the surface has been evaluated over the
appropriate spatial area,31 the GS
facility must determine through site
characterization and computational
modeling the spatial area that may be
impacted by the CO2 injection activity
over the lifetime of the project,
accounting for the physical and
chemical properties of all phases of the
injected CO2 stream. This spatial area
must be determined to account for all
potential leakage pathways, including
wells. If the GS facility is producing oil
or gas, the spatial area would also need
30 2006 IPCC Guidelines for National Greenhouse
Gas Inventories: Volume 2—Energy. Chapter 5
Carbon Dioxide Transport, Injection, and Geological
Storage. Available at: https://www.ipccnggip.iges.or.jp/public/2006gl/index.htm; see also
UIC Class VI proposal, 73 FR 43492 (July 25, 2008).
31 EPA recognizes that surface rights access to the
entire spatial area required for site characterization
and monitoring may not conveniently rest with the
owner or operator of the CO2 injection wells (i.e.,
the GS facility reporter in subpart RR). Issues
associated with surface and pore space ownership
are outside the scope of this proposed rule.
However, the Agency recognizes that the MRV plan
will need to take into account the relevant
ownership rights and property access.
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to contain the production wells
associated with CO2 injection.
EPA is proposing that the GS facility
would be required to re-evaluate and remodel the spatial area of evaluation at
least every ten years or to describe the
rationale for a different frequency in its
MRV plan and, once approved, apply
that frequency. Requiring re-evaluation
of the spatial area of monitoring through
updating simulation models with new
monitoring data will provide the most
accurate representation of subsurface
CO2 movement.
EPA seeks comment on the proposed
re-evaluation frequency and whether the
spatial area required for site
characterization is adequate to detect
and quantify potential leakage to the
surface. Specifically, EPA seeks
comment on whether there will be cases
in which the spatial area should be
larger to detect unexpected leakage to
the surface beyond the pressure front
boundary. Alternatively, EPA seeks
comment on whether the spatial area
should be larger than the lateral extent
of the CO2 plume, but smaller than the
area defined by the pressure front. EPA
also seeks comment on whether the
spatial area should be defined by the
lateral extent of the CO2 plume.
The MRV plan should include a
description of the site characterization
that confirms that the geology and the
local and regional hydrogeology of the
GS facility have been evaluated and that
explains how the spatial area was
established. This should include a
narrative description of the geologic
formation(s) along with simple
stratigraphic depictions showing
formation depths and locations,
information on the presence of an
effective confining system 32 overlying
the injection zone,33 and a map showing
32 A confining system is a geological formation,
group of formations, or part of a formation that is
comprised of impermeable or distinctly less
permeable material stratigraphically overlying the
injection zone that acts as a barrier to CO2
movement. (73 FR 43492).
33 The injection zone is a geologic formation,
group of formations, or part of a formation that is
of sufficient areal extent, thickness, porosity, and
permeability to receive carbon dioxide through a
well or wells associated with a GS project. (73 FR
43492).
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Required under subpart RR
proposal
the modeled spatial area of evaluation
over the lifetime of the project.
The MRV plan should also
demonstrate to EPA that all potential
leakage pathways for CO2 escape to the
surface from the injection zone in the
spatial area have been identified and
characterized. Wells (and other artificial
penetrations such as boreholes) are one
of the most probable conduits for the
escape of CO2 from the injection zone.34
If a well penetrates the confining
system, the site characterization should
include an assessment of supporting
documentation such as well
construction and plugging. Faults and
fractures that are natural or that may be
induced by pressure changes may also
serve as pathways for CO2 leakage out
of the confining zone and to the surface.
Additionally, geologic heterogeneities,
such as high permeability zones in the
confining system or an insufficient
lateral extent of the confining system,
may be potential leakage pathways for
CO2. The MRV plan should include the
location and depth of all potential
leakage pathways along with a
qualitative description of their
condition. For more information on
leakage pathways, see the monitoring
plan TSD.35 The MRV plan should
include an overview of the methods
used to characterize the site; actual data
can but does not need to be initially
submitted.
Finally, the risk assessment
component of the MRV plan should
34 Gasda, SE, S Bachu and MA Celia. 2004. ‘‘The
potential for CO2 leakage from storage sites in
geological media: Analysis of well distribution in
mature sedimentary basins,’’ Environmental
Geology 46 (6–7), pp. 707–720; Benson, SM. 2005.
‘‘Monitoring to Ensure Safe and Effective Geologic
Sequestration of Carbon Dioxide,’’ IPCC Workshop
on Carbon Dioxide Capture and Storage; IPCC.
2005. ‘‘IPCC Special Report on Carbon Dioxide
Capture and Storage,’’ by Working Group III of the
Intergovernmental Panel on Climate Change.
Available at: https://www1.ipcc.ch/ipccreports/
srccs.htm; Carey, J, M Wigand, SJ Chipera, G
WoldeGabriel, R Pawar, PC Lichtner, SC Wehner,
MA Raines, GD Guthrie, Jr. 2007. ‘‘Analysis and
performance of oil well cement with 30 years of
CO2 exposure from the SACROC Unit, West Texas,
USA.’’ 8th International Conference on Greenhouse
Gas Control Technologies, International Journal of
Greenhouse Gas Control Volume 1, Issue 1, April
2007, Pages 75–85.
35 Monitoring Plans for Geologic Sequestration
TSD (see docket ID No. EPA–HQ–OAR–2009–0926).
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include an overview of the methods
used to model the subsurface behavior
of CO2 and the modeling results that
estimate the timing, location, route and
flux of potential leakage to the surface.
It should include a brief overview of the
input data quantity and the level of
uncertainty associated with the models,
as well as sensitivity analysis to assess
the range of potential CO2 leakage
emissions.
Strategy for Detecting and
Quantifying CO2 Leakage to the Surface.
EPA is proposing that the MRV plan
must provide a strategy for leak
detection. The MRV plan would include
the methodology for, rationale for, and
frequency of monitoring that will be
conducted to detect potential leakage of
CO2 to the surface. The strategy for leak
detection should be based on the risk
assessment required in this Section
II.D.3 of this preamble and be targeted
to where and when leakage to the
surface is most likely to occur.
Therefore, the MRV plan should also
describe the methodology for, rationale
for, and frequency of evaluation of the
entire spatial area of the GS facility to
detect any CO2 emissions from
unexpected leakage pathways. The MRV
plan should describe the monitoring
technologies that will be employed at
the facility, the assumed detection
limits of the technologies, the
monitoring locations, spatial array, and
frequency of sampling. The MRV plan
should provide the rationale and
justification for each of these choices. A
leak detection strategy that adequately
meets this proposed rule’s requirements
may include a combination of
subsurface, vadose zone, soil zone,
ocean, surface water, and/or
atmospheric monitoring and modeling.
For the purposes of this proposed rule,
CO2 leakage to the surface includes CO2
emitted to the atmosphere, CO2 emitted
to the ocean from the sub-seabed, CO2
emitted to surface water, and CO2
emitted to indoor air environments. The
Agency notes that continuous air
monitoring or mitigation is not required
by this proposal.
Even though only the CO2 that leaks
to the surface must be quantified for this
proposed rule, information about the
movement of CO2 in the subsurface and
near-surface can serve as an early
warning of a potential leak at the
surface. This information will lead to a
better understanding of the GS facility
and the anticipated movement of the
CO2 plume, and it will help to pinpoint
the area and the timing in which a
potential leak to the surface may occur.
This in turn will inform where
monitoring for leak detection at the
surface must be deployed.
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For example, sampling at a deep
monitoring well may indicate migration
of the CO2 out of the confining system.
Though this monitoring result does not
necessarily mean that CO2 will
eventually leak to the surface, the GS
reporter would use this information on
the sub-surface movement of CO2 to
deploy monitoring equipment according
to the strategy outlined in the MRV plan
in case detection and quantification of
CO2 leakage to the surface is necessary.
Generally, an iterative process should
be in place to update the predictive
models by applying results of ongoing
monitoring. The GS reporter needs to
consider how the monitoring results
will change the leak detection and
quantification strategies in the MRV
plan approved by EPA. Adjustments to
the MRV plan may result from updates
to the models that were used to identify
the leakage pathways, assess the risk of
leakage, and predict the scope of
potential leakage scenarios. If the MRV
plan is adjusted in these circumstances,
the reporter must submit an addendum
to EPA that describes how the leak
detection and quantification strategy
was adjusted (see Section II.E of this
preamble for more detail).
EPA is proposing that the MRV plan
would not need to include methods for
monitoring fugitive and vented CO2
emissions from surface equipment (e.g.,
CO2 compression systems) at GS
facilities because, in EPA’s view, those
methods need not vary from site to site
in order to estimate emissions
effectively. Universal methods are
proposed in subpart W, and those
methods would be used to quantify
fugitive and vented CO2 emissions from
surface equipment and to report those
emissions under subpart W or subpart
RR as appropriate (see Section II.C of
this preamble).
If a CO2 leak is detected at the surface,
the GS reporter must quantify the
amount of CO2 leaked. EPA considered
three alternatives for reporting CO2
leakage: assuming that all injected CO2
remains sequestered, assuming that a
proportion of injected CO2 remains
sequestered, and reporting of CO2
leakage based on site-specific
monitoring. EPA outlines the
advantages and disadvantages of each
alternative and seeks comment and data
on each alternative, as well as any
alternatives not discussed.
Under the first alternative, EPA would
rely on published information and
existing studies to assume that all
injected CO2 remains sequestered. EPA
would assume these results can be
generalized to all GS projects. EPA notes
that international guidelines on
information collection and reporting
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18591
efforts outlined in Section I.E of this
preamble do not support this approach.
Furthermore, EPA did not propose this
approach because of the limited
empirical data and the variability in
geology, site management and/or
business practices, and other conditions
among GS facilities. In addition,
assuming that all injected CO2 remains
sequestered would not take into account
potential fugitive or vented emissions
from surface equipment or CO2
produced from oil or gas production
wells, during or after operations.
Under the second alternative, EPA
would assume that a proportion of
injected CO2 remains sequestered. EPA
would assume that this proportion can
be generalized to all GS projects.
International guidelines on information
collection and reporting efforts outlined
in Section I.E of this preamble do not
support this approach. Furthermore,
EPA did not propose this approach
because of the limited empirical data
and the variability in geology, site
management and/or business practices,
and other conditions among GS
facilities. EPA also seeks comment and
data on whether a sequestration factor
could be applied to ER operations in
cases where CO2 injection and site
operations are not specifically designed
with GS in mind.
The third approach, and the approach
EPA is proposing today, is that the MRV
plan describe the approaches that the
GS reporter will take to quantify CO2
emissions if leakage is detected. The
approach should be specific to the type
of potential leak. For example, for point
sources of CO2 (e.g., leakage from wells),
bagging or tenting methods could be
used. EPA recognizes that quantifying
CO2 emissions and distinguishing CO2
leakage from background emissions is
challenging, but necessary for the
purposes of determining the total
amount of CO2 that is sequestered at a
GS facility. EPA is proposing that a leak
could be quantified through estimation
or by direct measurement and seeks
comment on allowing either estimation
or direct measurement for quantifying a
leak.
In cases where a leak is not quantified
by estimation, EPA is proposing that if
a leak is detected, the reporter must
assume that the duration of the leak is
equal to the duration between
demonstrated null monitoring results
unless subsurface monitoring can be
used to provide a better indication on
the timing of the leak. EPA finds this
conservative approach reasonable
because the estimate of the duration of
the leak directly influences the estimate
of the amount of CO2 emitted to the
surface. The Agency recognizes that this
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approach could overestimate emissions
of CO2. EPA considered requiring that
the MRV plan include a site-specific
strategy for determining duration of any
leakage detected in cases where a leak
is not determined by estimation, but
EPA concluded that this approach
would allow too much variation in
reporting on CO2 leakage (if any occurs)
and would make the quantities of CO2
reported as sequestered less comparable.
EPA seeks comment on the selected
approach for determining the duration
of the leak event and the alternatives.
EPA is proposing that if multiple CO2
leaks to the surface occur in a reporting
year, the mass of each leak should be
quantified and the totals then aggregated
for reporting.
An approach for an uncertainty
assessment of the leakage estimates and
measurements derived from the
proposed modeling and monitoring at
the GS facility should also be included
in this component of the MRV plan.
As further outlined in Section II.E of
this preamble, EPA is proposing that if
leakage is detected during a given
reporting year, the GS reporter must
submit an annual report addendum to
coincide with submission of the next
annual report (March 31 of a following
year).
Strategy for Establishing Pre-Injection
Environmental Baselines. EPA is
proposing that the MRV plan describe
when and how pre-injection
environmental baselines would be
established based on the strategy for
leak detection described in this section
of the preamble. The GS reporter is
required to establish baselines at
potential leakage pathways (based on
the risk of leakage from these pathways),
and over the entire spatial area of
evaluation for periodic evaluation of
unidentified leakage pathways. Preinjection baselines will be used to
evaluate the performance of the site and
are essential to detect CO2 leakage from
the site.
CO2 is ubiquitous in the environment
and concentrations may vary over space
and time (e.g., diurnally, seasonally,
annually). Therefore, determining
background levels of CO2 and
understanding natural fluctuations is
necessary to discern whether detected
CO2 is attributable to leakage or to
preexisting sources. It is also important
to establish baselines before injection
because many of the instruments used
to monitor CO2 at the surface do not
measure fluxes of CO2 directly; rather,
the instruments are useful for tracking
the injected CO2 because one can
compare parameters before and after
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injection and over time.36
Environmental baselines at the facility
before injection must reflect diurnal,
seasonal, and annual changes in not
only the levels of CO2 but also in other
relevant surface and/or near-surface
conditions (e.g., wind speed). Baseline
monitoring could also include gas
composition and isotopic analysis of
any background fluxes of CO2, which
may be useful for distinguishing
between natural (biogenic or
thermogenic) and anthropogenic CO2.37
There may be cases in which CO2
injection has taken place for some time
(potentially years, as in the case of
currently operating ER projects) and the
baseline was not evaluated preinjection. EPA is proposing that a
facility in this situation would outline
in this component of the MRV plan
alternatives to establishing pre-injection
baselines. In such situations,
alternatives to characterizing baseline
conditions could include identification
of proximal locations where diurnal,
seasonal, and annual measurements that
are assumed to be similar to preinjection conditions at the site can be
taken. This technique was used by a site
that detected annual CO2 emissions of
about 3,800 tonnes/year (0.01 percent of
total injected CO2) from surface
monitoring but could not compare the
flux to a pre-injection baseline to
determine what percentage was
attributable to injected CO2.38 Other
approaches could include permanent
continuous monitor networks with
upwind and downwind correlation or
mobile monitoring capable of
determining local ambient background
levels. EPA recognizes the challenge in
establishing a baseline in these cases
and seeks comment on this proposed
case-by-case approach and on whether
real-time determination of
36 Benson, S, E Gasperikova, and M Hoversten.
2004. ‘‘Overview of Monitoring Techniques and
Protocols for Geologic Storage Projects.’’ Prepared
for the IEA GHG Programme. PH4–29; Johnson, J.
2009. ‘‘Integrated modeling, monitoring, and site
characterization to assess the isolation performance
of geologic CO2 storage: Requirements, challenges,
and methodology.’’ Energy Procedia 1:1855–1861;
Forbes, S, P Verma, T Curry, J Friedman, S Wade.
2008. ‘‘Guidelines for carbon dioxide capture,
transport, and storage.’’ World Resources Institute.
Available at: https://pdf.wri.org/ccs_guidelines.pdf.
37 American Petroleum Institute and International
Petroleum Industry Environmental Conservation
Association. 2007. ‘‘Oil and Natural Gas Industry
Guidelines for Greenhouse Gas Reduction Projects
Part II: Carbon Capture and Geological Storage
Emission Reduction Family,’’ June, 2007.
38 Klusman, RW. 2003. ‘‘Rate measurements and
detection of gas microseepage to the atmosphere
from an enhanced oil recovery/sequestration
project, Rangely, Colorado, USA.’’ Applied
Geochemistry, volume 18, issue 12.
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environmental baseline upwind of
potential leakage is preferred.
Tailor Mass Balance Equation for
Sequestration. As explained in Section
II.C of this preamble, a GS reporter
would be required to report the annual
amount of CO2 sequestered at a facility
using a mass balance equation, in which
the sum of CO2 emissions would be
subtracted from the amount of CO2
injected to equal the amount of CO2
sequestered. A specific mass balance
equation is provided in the regulatory
text, to which the facility must apply
site-specific variables based on
operational conditions. Accordingly,
EPA is proposing that a GS reporter
must consider whether any fugitive or
vented CO2 surface emissions were
measured downstream of the injection
flow meters (i.e., between the injection
flow meter and the injection well). If so,
these quantities should not be
accounted as stored and should be
subtracted from the mass balance
equation as a variable. A GS facility
with ER operations must additionally
consider whether any fugitive or vented
CO2 emissions were measured upstream
of the production flow meters (i.e.,
between the production well and the
separator) and how much produced CO2
is not successfully measured by the
production flow meter because it
remains dissolved in the produced oil or
gas. For ER operations, these quantities
should not be accounted as stored and
should also be subtracted from the mass
balance equation as variables.
EPA is proposing that GS reporters be
required to include a written summary
of these considerations, including any
assumptions made and methodologies
used to calculate these site-specific
variables over the reporting year.
4. MRV Plan Approval Process
EPA is proposing to evaluate each
MRV plan to ensure that the GS facility
has an appropriate strategy in place to
effectively quantify geologically
sequestered CO2. EPA will evaluate the
adequacy of the methodologies
proposed to detect and quantify leakage,
including whether the chosen
monitoring technologies are suitable for
the type of leakage pathway and for the
type of risk evaluated at that pathway.
This proposal is being conducted
under CAA section 114. As such, it does
not require control measures,
remediation, or any other actions that
would alter operations at a facility. In
order to develop, gain approval of, and
implement its MRV plan, a GS facility
would not be expected to shut down or
delay its operations. EPA developed the
proposed reporting requirements with
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consideration for business-as-usual
operations in order to minimize burden.
Although MRV plan approval would
be an inherently EPA function, the
Agency is considering approaches and
processes to streamline and facilitate
external technical input in the
development of specific evaluation
criteria or guidelines, particularly at the
outset of the program. EPA recognizes
that an adaptive approach to the GS
portion of this proposal will be
necessary to take advantage of the
experience gained in developing and
implementing MRV plans and in
complying with the proposed UIC Class
VI requirements. EPA expects to update
the guidelines and requirements of an
MRV plan over time as technologies,
methodologies, and scientific
understanding of GS evolve; and the
Agency believes that the site-specific
nature of the MRV plan enables the
proposed approach to adapt and
improve over time.
E. Selection of Schedule and Process for
Reporting
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1. First Tier Reporting Requirements for
Injection Facilities
All injection facilities that meet the
definitions in subpart RR and that are in
active operation when this proposed
rule is finalized would begin collecting
data on CO2 injected, CO2 transferred
from offsite, and source of CO2, if
known, on January 1, 2011, covering a
period between January 1 to December
31. Data would be submitted to EPA by
operating facilities in an annual report
on each March 31 of each calendar year,
beginning with March 31, 2012, for data
collected in the previous calendar year.
The Agency plans to issue the final
rule in sufficient time for existing
injection facilities to prepare for
monitoring and reporting before January
1, 2011, and to begin monitoring CO2
injection and CO2 transferred from
offsite on January 1, 2011. Preparation
would include studying the final rule,
determining whether it applies to the
facility, identifying the requirements
with which the facility must comply,
and preparing to monitor and collect the
required data needed to calculate and
report GHG emissions. However, EPA
recognizes that meeting that goal may be
challenging and seek comments on
alternative effective dates.
The date on which a new facility
begins injecting CO2 is the date on
which a new facility must begin
monitoring the first tier of requirements
for subpart RR. The annual report
submitted by the new facility on March
31 of the year following start-up
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therefore may include data for only part
of the year.
2. Second Tier Reporting Requirements
for GS Facilities—Submission,
Approval, and Reporting
EPA is proposing that all GS facilities
and any injection facilities that opt-in to
the GS monitoring and reporting
requirements would submit MRV plans
to EPA and seek EPA approval. Where
the GS facility would be relying on a
new UIC Class VI permit for MRV plan
requirements, EPA anticipates that the
MRV plan review would be conducted
concurrently with the UIC Class VI
permit review. EPA would require the
unique identification number associated
with the permit application and
notification of approval of the UIC Class
VI permit. Once an MRV plan is
approved by EPA, the GS facility would
implement it and then begin collecting
data on CO2 emitted and CO2
sequestered. Finally, the reporter would
include this additional quantitative data
in the first annual report submitted to
EPA after the approved MRV plan has
been implemented and in all subsequent
annual reports. An annual report
addendum would also be required to be
submitted if the GS facility triggered any
of the addendum submission
requirements outlined in this proposal.
The Agency seeks to establish an
MRV plan submission and approval
schedule that allows the GS facility
reporter to implement its plan without
delay. Therefore, EPA is proposing a
rolling schedule for submission of the
MRV plan to EPA whereby the reporter
could submit the plan to EPA on any
calendar date. From the date submitted,
EPA would determine if the application
is complete, review the plan, work with
each reporter to ensure that the MRV
plan appropriately addresses the
requirements, and revise the plan
accordingly. This interactive process
would be limited to a reasonable time
period, after which EPA would approve
a revised MRV plan.
EPA is proposing to provide for an
appeal process in situations where the
GS facility does not agree with the
Agency’s approved plan. One option
would be for a reporter to request a
formal administrative review (and if
appropriate, an evidentiary hearing)
with the Environmental Appeals Board
using the appeal procedures provided in
40 CFR Part 78. Under this approach,
filing an appeal and exhausting all
administrative remedies would be a
prerequisite to seeking judicial review.
Another option would allow the
reporter to appeal directly with the
appropriate court, pursuant to CAA
section 307(b)(1). EPA seeks comment
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on both options for resolving disputes
regarding MRV plans, or whether any
alternative, expedited process is more
appropriate.
EPA is proposing that the GS facility
must begin implementing the MRV plan
within thirty days of EPA approval.
Because implementation may require
more than thirty days (e.g., in order to
establish environmental baselines), it is
possible that implementation would not
be completed within 30 days of EPA
approval, depending on the MRV plan;
the facility would follow
implementation as set forth in the
facility’s MRV plan. If the MRV plan is
appealed, EPA is proposing to require
the GS facility to begin implementation
of the approved plan until such a time
that the MRV plan appeal process is
complete. EPA seeks comment on
whether the implementation of the MRV
plan should be delayed until the appeal
is resolved.
Every annual report submitted by the
GS facility after MRV plan
implementation begins would include
both the first tier of data required of all
CO2 injection facilities and the second
tier of data related to GS. In the first year
following initial MRV plan
implementation, it is possible that the
GS-related data collected and reported
may only cover part of the year.
EPA is proposing that an injection
facility opting in to the GS portion of
this proposed rule may submit an MRV
plan at any time. All other GS facilities
will be required to submit an MRV plan
to EPA (A) within six months from the
time that their UIC permitting authority
confirms the area of review or (B) by
December 31 of the year that the UIC
permitting authority confirms the area
of review, whichever date is later. If
such facilities already have a UIC permit
as of the date of publication of the final
subpart RR in the Federal Register, they
must submit the MRV plan to EPA
within six months of the date of
publication of this subpart. This
submission deadline would allow the
facility to implement all monitoring
required by EPA as quickly and
seamlessly as possible, and in parallel
with a facility’s UIC permit
requirements. All facilities that are
required to submit an MRV plan to EPA
will be allowed to request an extension
of up to an additional six months. In the
case of a facility that is not under the
jurisdiction of the SDWA, the MRV plan
submission schedule would be based on
the facility’s relevant permit, rather than
a UIC permit. EPA seeks comment on
this approach for MRV plan
submissions and on whether an
alternative deadline, such as a
submission deadline based on when a
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GS facility’s UIC permit is issued,
would be more appropriate and
efficient.
EPA seeks comment on the proposed
rolling submission process and whether
an alternative would be more
appropriate. For example, GS facilities
(both required and opt-in facilities)
could be required to submit an MRV
plan by a specific date or within a
specific window of time each calendar
year if they plan to begin operating in
the subsequent calendar year.
3. Second Tier Reporting Requirements
for GS Facilities—Post Implementation
Once a reporter begins implementing
an EPA-approved MRV plan, it may be
required to submit additional
information to EPA, either through an
annual report addendum, or through resubmitting a revised MRV plan for EPA
approval.
When a reporter initially develops an
MRV plan, it does so based on its
existing understanding of the GS facility
site characterization and in some cases
previous experience with CO2 injection,
modeling, and monitoring. When EPA
reviews the plan, it evaluates whether
the procedures proposed will result in
the most effective collection of data
possible and practical, given this
existing understanding. However, EPA
recognizes that a reporter’s
understanding of the GS facility may
evolve because of new information or
altered site conditions. Under these
circumstances, the site should continue
to prioritize the most effective collection
of data possible and practical, even if it
requires an adjustment in the
monitoring procedures used. The site
would implement these adjustments as
needed and would inform EPA about
them via an annual report addendum,
submitted at the same time as the next
annual report (March 31 of the
subsequent calendar year). An annual
report addendum should also describe
changes to the spatial area of
monitoring. Data reporting should not
be disrupted as a result. EPA is
proposing that the annual report
addendum will not require EPA
approval.
A reporter would also be required to
submit an annual report addendum if
leakage is detected. The addendum
should outline the procedures or
equipment that detected the leakage,
what assumptions were made to
quantify the detected leakage to the
surface, including assumptions about
when the leak began and the duration of
the leak, and any adjustment made to
the MRV plan. If the number reported
for leakage represents more than one
leakage event, the addendum should
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describe how each leak was detected
and quantified.
In general, the MRV plan should be
revised as experience is gained over the
course of the project (for example, as
monitoring results are used to validate
and update model predictions) and
should keep pace with the development
of monitoring instruments and methods.
These revisions will be shared with EPA
through annual report addenda.
EPA seeks comment on whether the
GS facility should resubmit an MRV
plan at a minimum frequency that
compiles all revisions over the previous
years into one updated document and
that undergoes an EPA approval
process. EPA seeks comment on
whether such a routine resubmission is
appropriate, and if so how the minimum
frequency for re-submittal should be
established. This minimum frequency
could be a fixed number for all facilities,
such as every ten years. Alternatively, it
could be established on a site-by-site
basis based on the reporter’s technical
justification or on the minimum
frequency associated with the reevaluation of the facility’s spatial area of
evaluation.
EPA is proposing that the MRV plan
must be revised and re-submitted to
EPA for approval if the reporter is out
of compliance with its UIC permit (or
relevant permit in the case of a facility
that is not under the jurisdiction of the
SDWA), or if EPA deems a resubmission
necessary as the result of an annual
report addendum received or an EPA
on-site audit conducted as part of the
MRR verification provisions. EPA seeks
comment on whether any other events
or conditions should require
resubmission of the MRV plan. In
addition, EPA is proposing that the GS
facility under its own volition could
submit a revised MRV plan in any
reporting year. Resubmitted MRV plans
would be accepted on a rolling basis just
as initial MRV plans.
4. Annual Reports
For this proposed rule, EPA seeks
quantitative data from all facilities in a
consistent format and at a consistent
level, in a timely fashion at the
beginning of every reporting year
(covering the previous year’s data) in
order to electronically verify the data,
publish it as authorized by the CAA,
and use the collected information for
the purposes described in this proposal.
Therefore, EPA is proposing that, as
with the other data reported in the MRR,
CO2 injection and sequestration data
would be reported directly to EPA
electronically via an annual report. EPA
is also proposing that MRV plans and
annual report addenda developed by GS
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facilities would be submitted
electronically to EPA. To minimize
redundancy and burden on industry,
EPA has considered the procedures,
methodologies, units, quality assurance
and quality control (QA/QC)
requirements, and formats required
under the UIC permit classes when
developing the requirements of this
proposed rule. EPA’s intention is that
reporters use the same data to meet the
reporting requirements of both programs
to the greatest extent possible.
All injection facilities would submit
reports with quantitative data annually
on an ongoing basis. The snapshot of
information provided by a one-time
information collection request would
not provide the type of ongoing
information which could inform the
variety of potential policy options being
evaluated for addressing climate change.
Due to the comprehensive reporting and
monitoring requirements in this
proposal, the Agency has concluded
that it is not appropriate to require
reporting of historical emissions data.
EPA proposed and evaluated comments
on this reporting provision under the
MRR. The historical data provision of
the MRR also applies to today’s
proposed rule.
Most voluntary and mandatory GHG
reporting programs include provisions
for operators to revise previously
submitted data. Under the final MRR,
EPA requires the reporter to submit a
revised report within 45 days of
discovering or being notified by EPA of
errors in an annual GHG report. The
revised report must correct all identified
errors. The reporter must retain
documentation for three years to
support any revisions made to an
annual GHG report. EPA proposed and
evaluated comments on this reporting
provision under the MRR. As a final
provision of that rule, the requirement
to submit a correct report within 45
days and retention of documentation for
three years applies to today’s rule.
The final MRR provides a mechanism
for facilities to exit the reporting
program when they are below a
reporting threshold for five or three
consecutive years, depending on the
exact emissions levels. Because of the
unique nature of CO2 injection and GS
activities as noted in the threshold
analysis discussion in Section II.B of
this preamble, EPA is proposing that
this provision would not apply to GS
facilities. Instead, EPA is proposing that
all CO2 injection facilities would be
allowed to cease reporting CO2 injection
upon the plugging of the injection well
or wells that constitute the facility. GS
facilities will be allowed to cease all
other reporting requirements under this
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subpart once the CO2 plume and
pressure front have stabilized. EPA will
accept demonstrations made to fulfill
UIC Class VI permit requirements in
order to meet requirements for ceasing
GS reporting under this proposal. EPA
seeks comment on this approach for
allowing facilities to cease reporting.
EPA recognizes that there are other
possible approaches. For example, the
Agency could conform the mechanism
that other facilities use for exiting the
MRR to subpart RR, allowing CO2
injection facilities that are not GS
facilities to cease reporting if they are
below an injection threshold for five or
three consecutive years, depending on
the exact injection levels. EPA did not
propose this alternative because of a
lack of data on the incidence and scale
of surface emissions and leakage.
Another approach would be to provide
a ‘‘no exit’’ approach for GS facilities,
which would allow EPA to obtain
valuable data on the long-term efficacy
of GS. EPA is not proposing a ‘‘no exit’’
approach because the Agency wanted to
provide an opportunity for reporters to
cease reporting. However, EPA seeks
comment on these alternative
approaches for allowing facilities to
cease reporting.
Each annual report developed under
this proposed rule would contain a
signed certification by a Designated
Representative of the facility. On behalf
of the reporter, the Designated
Representative would certify under
penalty of law that the report has been
prepared in accordance with the
requirements of 40 CFR part 98 and that
the information contained in the report
is true and accurate, based on a
reasonable inquiry of individuals
responsible for obtaining the
information. EPA proposed and
evaluated comments on these reporting
provisions under the MRR. As final
provisions of the MRR, they apply to
today’s proposal.
Representative to certify that the data
reported is accurate to the best of his/
her knowledge.
For this proposed rule, EPA is
proposing that the data submitted by GS
facilities may be evaluated and verified
manually by EPA along with the
qualitative contents of the MRV plan
(see Section II.D of this preamble). It
may be that electronic verification of GS
data would not be adequate to verify
whether the EPA-approved MRV plan
was followed and whether any leakage
was detected in the reporting year at a
particular facility. EPA seeks comment
on manual evaluation of data and
qualitative elements of an MRV plan.
5. Data Verification
In the MRR, EPA will verify emissions
data electronically using numerous
approaches such as: Executing
equations and comparing the results to
reported data; comparing reported data
to a realistic data range; comparing
trends in reported data across years;
comparing data from one year across
reporters; conducting a pass/fail check
on binary data; collecting secondary
data that can proxy emissions; and
conducting statistical analysis to
identify outliers. EPA may conduct
selective audits on facilities whose data
raises questions during the verification
process. In addition, all reporting
entities will select a Designated
F. Selection of Procedures for Estimating
Missing Data
EPA has concluded that it is
important to have missing data
procedures in order to ensure a
complete report of amounts of CO2 and
emissions from a particular facility. In
this rule, EPA is proposing missing data
procedures for the quarterly values of
mass or volume and concentration of
these streams, and CO2 transferred from
offsite. EPA is proposing that these
procedures can be used by all injection
facilities, including GS facilities. EPA is
also proposing procedures for missing
data on CO2 production from GS
facilities. EPA seeks comment on these
procedures and on whether it is
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6. Confidential Business Information
(CBI)
EPA’s public information regulations
contain a definition of ‘‘emissions data’’
at 40 CFR 2.301, and EPA has discussed
in an earlier Federal Register notice
what data elements constitute emissions
data that cannot be withheld as CBI (56
FR 7042–7043, February 21, 1991).
While determinations about whether
information claimed as CBI and whether
the information meets the definition of
emissions data are usually made on a
case-by-case basis, EPA recognizes that
such an approach would be
cumbersome given the scope of the MRR
and the compelling need to make data
that are not CBI, or are emissions data,
available to the public. For this reason,
EPA will be initiating a separate notice
and comment process to make CBI and
emissions data determinations for the
categories of data collected under the
MRR.
As stated in the MRR, EPA will
protect any information claimed as CBI
in accordance with regulations in 40
CFR part 2, subpart B. However, in
general, emissions data collected under
CAA section 114 shall be available to
the public and cannot be withheld as
CBI.
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18595
appropriate to provide missing data
procedures for GS facilities.
EPA is not proposing missing data
procedures for leakage quantification.
EPA is proposing that the MRV plan
include quantification methods and
assumptions for all potential leakage
scenarios. If leakage is detected for
which a quantification approach is not
outlined in the plan, this information
must be included in the addendum.
G. Selection of Records To Retain
EPA is proposing that, in addition to
the records required by § 98.3(g), each
facility must retain quarterly records of
injected CO2 and CO2 transferred from
offsite sources, including mass flow or
volumetric flow at standard conditions
and operating conditions, operating
temperature and pressure, and
concentration of these streams. EPA is
proposing that GS facilities would also
retain quarterly records of produced
CO2, if applicable, including mass flow
or volumetric flow at standard
conditions and operating conditions,
operating temperature and pressure, and
concentration of these streams; annual
records of the emitted CO2 from
subsurface geologic formation leakage
pathways; and any other records as
outlined for retention in your MRV
plan. EPA seeks comment on these
record retention requirements.
III. Economic Impacts of the Proposed
Rule
This section of the preamble examines
the costs and economic impacts of the
proposed rulemaking for CO2 injection
and GS and the estimated economic
impacts of the rule on affected entities,
including estimated impacts on small
entities. Complete detail of the
economic impacts of the proposed rule
can be found in the text of the economic
impact analysis (EIA) (EPA–HQ–OAR–
2009–0926). EPA seeks comment on the
methodology and data used for the
analysis.
A. How were compliance costs
estimated?
1. Summary of Method Used To
Estimate Compliance Costs
EPA estimated costs of complying
with this proposed rule and the total
incremental annual cost of compliance.
A base case is created assuming relevant
monitoring costs required under UIC
requirements (including the UIC Class
VI proposal). Then incremental
reporting from geologic storage sites
were evaluated in terms required
technologies, practices, and costs.
The estimated costs include capital
and operating and maintenance (O&M)
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including labor costs. The cost of
drilling and equipping wells represents
a large component of sequestration
costs. Examples of other costs include
seismic data acquisition, periodic
sampling and testing of the injected
CO2.
The estimated costs are based on
hypothetical or pro-forma sites for
various types of projects such as R&D
GS projects, commercial saline
formation projects, and ER GS projects.
The geologic and engineering
assumptions for these pro-forma
projects are the same as those used by
the EPA Office of Water in the proposed
UIC Class VI rule for CO2 injection
wells. The costs are presented in 2008
dollars.
The capital costs are annualized using
an interest rate of 7% with projects
lasting 7 years or 20 years. Next, annual
O&M costs are added to the annualized
capital costs to determine total annual
direct costs. Finally, a 20 percent
overhead and general and
administrative cost factor is added to
obtain total annual costs. These are then
divided by the amount assumed to be
injected each year in the pro-forma
project to arrive at total costs per metric
ton of CO2 injected. These per-ton costs
are then used to estimate total annual
costs for the level of injection expected
in the activity baseline.
B. What are the costs of the proposed
rule?
1. Summary of Costs
The total annualized costs incurred
under the rule by these entities would
be approximately $714,000 ($2008
dollars), as illustrated in Table 7 of this
preamble. The public sector burden
estimate is $344,000 for program
implementation and verification
activities. This may underestimate the
total public sector burden depending on
the extent to which DOE R&D projects
funded with public dollars transition to
demonstration or commercial GS, and
consequently incur costs associated
with monitoring, reporting and
verification. Given uncertainties related
to project adoption and the costs of the
reporting program, EPA considered two
other private cost scenarios (one higher
and one lower than the reference cost
scenario) in order to assess a range of
economic impacts on affected entities,
as illustrated in table 8 of this preamble.
TABLE 7—NATIONAL ANNUALIZED MANDATORY REPORTING COSTS ESTIMATES (2008$): SUBPART RR
Type
Number of
projects
Metric tons
CO2 injected
per year
R&D .............................................................................................................................................
CO2 Injection Facilities (no GS) 1 ................................................................................................
Private Sector, Total All Projects .................................................................................................
Private Sector, Average ($/ton) ...................................................................................................
Public Sector, Total .....................................................................................................................
National Total ...............................................................................................................................
9
80
89
........................
........................
........................
Total annual
cost
(thousand,
2008$)
5,320,000
36,815,442
45,435,442
........................
........................
........................
1 Includes
37
332
369
0.01
344
714
Class II ER Facilities.
TABLE 8—ANNUALIZED REPORTING COSTS PER PROJECT (2008$): SUBPART RR
Average
Alternative cost scenarios
Type
Reference
($1,000)
GS Facilities (commercial saline) 1 ..............................................................................................
GS Facilities (ER opt in) ..............................................................................................................
CO2 Injection Facilities 1 ..............................................................................................................
1 Includes
289
1,679
4
Low
($1,000)
High
($1,000)
7
1,485
4
470
1,804
4
Class II ER Facilities.
C. What are the economic impacts of the
proposed rule?
1. Summary of Economic Impacts
EPA assessed how the regulatory
program may influence the profitability
of companies by comparing the
monitoring program costs to total sales
(i.e., a ‘‘sales’’ test). Given limited data
on commercial GS operations, EPA
restricted the analysis to ER operations
(approximately 90 percent of the fields).
To do this, EPA divided the average
annualized mandatory reporting costs
per field by the estimated revenue for a
representative field. Sales test ratios are
between 3.1 to 3.3 percent for GS
facilities (ER opt in). In contrast, ER CO2
injection facilities (no GS) sales test
ratios are below 0.01 percent, as
illustrated in Table 9 of this preamble.
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TABLE 9—ESTIMATED ANNUAL REVENUE FOR A REPRESENTATIVE COMMERCIAL ER FIELD OPERATION (2008$)
Cost-to-Sales Ratios (CSRs)
Alternative cost scenarios
Reference
(percent)
GS Facilities (ER opt in) ..............................................................................................................
CO2 Injection Facilities (no GS) 1 ................................................................................................
1 Includes
3.1
<0.01
Class II ER Facilities.
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Low
(percent)
2.7
<0.01
High
(percent)
3.3
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D. What are the impacts of the proposed
rule on small businesses?
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1. Summary of Impacts on Small
Businesses
As required by the RFA and SBREFA,
EPA assessed the potential impacts of
the rule on small entities (small
businesses, governments, and non-profit
organizations). (See Section IV.C of this
preamble for definitions of small
entities.)
After considering the economic
impact of the rule on small entities, EPA
has concluded that this action will not
have a significant economic impact on
a substantial number of small entities.
Currently EPA believes small ER
operations will most likely be UIC Class
II ER projects. As shown in Table 9 of
this preamble, the average ratio of
annualized reporting program costs to
revenues of a typical ER operation likely
owned by a representative small
enterprise was less than 0.1%.
Although this rule will not have a
significant economic impact on a
substantial number of small entities,
EPA nonetheless took several steps to
reduce the impact of this rule on small
entities. For example, EPA is proposing
monitoring and reporting requirements
that build off of the UIC program. In
addition, EPA is proposing equipment
and methods that may already be in use
by a facility for compliance with its UIC
permit. Also, EPA is requiring annual
reporting instead of more frequent
reporting.
In addition to the public hearing that
EPA plans to hold, EPA has an open
door policy, similar to the outreach
conducted during the development of
the proposed and final MRR. Details of
these meetings are available in the
docket (EPA–HQ–OAR–2009–0926).
E. What are the benefits of the proposed
rule for society?
EPA examined the potential benefits
of this proposed rule. EPA’s previous
analysis of the MRR discussed the
benefits of a reporting system with
respect to policy making relevance,
transparency issues, market efficiency.
Instead of a quantitative analysis of the
benefits, EPA conducted a systematic
literature review of existing studies
including government, consulting, and
scholarly reports.
The greatest benefit of mandatory
reporting of industry GHG emissions to
government will be realized in
developing future GHG policies. For
example, in the EU’s Emissions Trading
System, a lack of accurate monitoring at
the facility level before establishing CO2
allowance permits resulted in allocation
of permits for emissions levels an
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average of 15 percent above actual levels
in every country except the United
Kingdom.
Benefits to industry of GHG emissions
monitoring include the value of having
independent, verifiable data to present
to the public to demonstrate appropriate
environmental stewardship, and a better
understanding of their emission levels
and sources to identify opportunities to
reduce emissions. Such monitoring
allows for inclusion of standardized
GHG data into environmental
management systems, providing the
necessary information to achieve and
disseminate their environmental
achievements.
Standardization will also be a benefit
to industry, once facilities invest in the
institutional knowledge and systems to
report emissions, the cost of monitoring
should fall and the accuracy of the
accounting should improve. A
standardized reporting program will
also allow for facilities to benchmark
themselves against similar facilities to
understand better their relative standing
within their industry.
IV. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Section 3(f)(1) of Executive
Order 12866 (58 FR 51735, October 4,
1993), this proposed action is not by
itself an ‘‘economically significant
regulatory action’’ because it is unlikely
to have an annual economic effect of
less than $100 million. EPA’s cost
analysis, presented in Section 4 of the
EIA, estimates that for the minimum
reporting under the recommended
regulatory option, the total annualized
cost of the rule will be approximately
$713,000 (in 2008$) during the first year
of the program and $713,000 in
subsequent years (including $0.3
million of programmatic costs to the
Agency). This proposed action adds
subpart RR to the MRR, which was a
significant regulatory action. Thus, EPA
has chosen to analyze the impacts of
subpart RR as if it were significant. EPA
submitted this proposed action to the
Office of Management and Budget
(OMB) for review under Executive
Order 12866, and any changes made in
response to OMB recommendations
have been documented in the docket for
this proposed action.
In addition, EPA prepared an analysis
of the potential costs associated with
this proposed action. This analysis is
contained in the ‘‘Economic Impact
Analysis for the Mandatory Reporting of
Greenhouse Gas Emissions Subpart RR’’
(EPA–HQ–OAR–2009–0926). A copy of
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the analysis is available in the docket
for this action and the analysis is briefly
summarized here. In this report, EPA
has identified the regulatory options
considered, their costs, the emissions
that would likely be reported under
each option, and explained the selection
of the option chosen for the rule.
Overall, EPA has concluded that the
costs of this proposed rule are
outweighed by the potential benefits of
more comprehensive information about
GHGs.
B. Paperwork Reduction Act
The information collection
requirements in this proposed rule have
been submitted for approval to the
Office of Management and Budget
(OMB) under the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. The
Information Collection Request (ICR)
document prepared by EPA has been
assigned EPA ICR number 2372.01.
EPA has identified the following goals
of the mandatory reporting system,
including:
• Obtain data that is of sufficient
quality that it can be used to analyze
and inform the development of a range
of future climate change policies and
potential regulations.
• Balance the rule’s coverage to
maximize the amount of emissions
reported while excluding small emitters.
• Create reporting requirements that
are, to the extent possible and
appropriate, consistent with existing
GHG reporting programs in order to
reduce reporting burden for all parties
involved.
The information from CO2 injection
and GS facilities will allow EPA to make
well-informed decisions about whether
and how to use the CAA to regulate
these facilities and encourage voluntary
reductions. Because EPA does not yet
know the specific policies that will be
adopted, the data reported through the
mandatory reporting system should be
of sufficient quality to inform policy
and program development. Also,
consistent with the Appropriations Act,
the reporting rule covers a broad range
of sectors of the economy.
This information collection is
mandatory and will be carried out under
CAA section 114. Information identified
and marked as Confidential Business
Information (CBI) will not be disclosed
except in accordance with procedures
set forth in 40 CFR Part 2. However,
emissions information collected under
CAA section 114 generally cannot be
claimed as CBI and will be made
public.39
39 Although CBI determinations are usually made
on a case-by-case basis, EPA has issued guidance
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The projected ICR cost and
respondent burden is $0.8 million and
4,510 hours per year. The estimated
average burden per response is 6.8
hours; the frequency of response is
annual for all respondents that must
comply with the rule’s reporting
requirements, except for electricitygenerating units that are already
required to report quarterly under 40
CFR Part 75 (acid rain program); and the
estimated average number of likely
respondents per year is 89. The cost
burden to respondents resulting from
the collection of information includes
the total capital and start-up cost
annualized over the equipment’s
expected useful life (averaging $0.1
million per year) a total operation and
maintenance component (averaging $0.3
million per year), and a labor cost
component (averaging $0.3 million per
year). Burden is defined at 5 CFR
1320.3(b).
These cost numbers differ from those
shown elsewhere in the EIA because
ICR costs represent the average cost over
the first three years of the rule, but costs
are reported elsewhere in the EIA for the
first year of the rule. Also, the total cost
estimate of the rule in the EIA includes
the cost to the Agency to administer the
program. The ICR differentiates between
respondent burden and cost to the
Agency.
An agency may not conduct or
sponsor, and a person is not required to
respond to, a collection of information
unless it displays a currently valid OMB
control number. The OMB control
numbers for EPA’s regulations in 40
CFR are listed in 40 CFR Part 9. When
this ICR is approved by OMB, the
Agency will publish a technical
amendment to 40 CFR part 9 in the
Federal Register to display the OMB
control number for the approved
information collection requirements
contained in the final rule.
To comment on the Agency’s need for
this information, the accuracy of the
provided burden estimates, and any
suggested methods for minimizing
respondent burden, EPA has established
a public docket for this proposed rule,
which includes this ICR, under Docket
ID number EPA–HQ–OAR–2009–0926.
Submit any comments related to the ICR
to EPA and OMB. See ADDRESSES
section at the beginning of this notice
for where to submit comments to EPA.
in an earlier Federal Register notice on what
constitutes emissions data that cannot be
considered CBI (956 FR 7042–7043, February 21,
1991). As discussed in Section II.R of the Final
MRR preamble, EPA will be initiating a separate
notice and comment process to make CBI
determinations for the data collected under this
proposed rulemaking.
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Send comments to OMB at the Office of
Information and Regulatory Affairs,
Office of Management and Budget, 725
17th Street, NW., Washington, DC
20503, Attention: Desk Office for EPA.
Since OMB is required to make a
decision concerning the ICR between 30
and 60 days after [date of publication],
a comment to OMB is best assured of
having its full effect if OMB receives it
by [publication plus 30]. The final rule
will respond to any OMB or public
comments on the information collection
requirements contained in this proposal.
C. Regulatory Flexibility Act (RFA)
The RFA generally requires an agency
to prepare a regulatory flexibility
analysis of any rule subject to notice
and comment rulemaking requirements
under the Administrative Procedure Act
or any other statute unless the agency
certifies that the rule will not have a
significant economic impact on a
substantial number of small entities.
Small entities include small businesses,
small organizations, and small
governmental jurisdictions.
For purposes of assessing the impacts
of today’s rule on small entities, small
entity is defined as: (1) A small business
as defined by the Small Business
Administration’s regulations at 13 CFR
121.201; (2) a small governmental
jurisdiction that is a government of a
city, county, town, school district or
special district with a population of less
than 50,000; and (3) a small
organization that is any not-for-profit
enterprise which is independently
owned and operated and is not
dominant in its field. Currently EPA
believes small ER operations will most
likely be CO2 injection facilities,
including Class II ER projects. The
average ratio of annualized reporting
program costs to revenues of a typical
ER operation likely owned by
representative small enterprises is less
than 1%
After considering the economic
impacts of today’s proposed rule on
small entities, I therefore certify that
this proposed rule will not have a
significant economic impact on a
substantial number of small entities.
Although this rule will not have a
significant economic impact on a
substantial number of small entities,
EPA nonetheless took several steps to
reduce the impact of this rule on small
entities. For example, EPA is proposing
monitoring and reporting requirements
that build off of the UIC program. In
addition, EPA is proposing equipment
and methods that may already be in use
by a facility for compliance with its UIC
permit. Also, EPA is requiring annual
reporting instead of more frequent
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reporting. In addition to the public
hearing that EPA plans to hold, EPA has
an open door policy, similar to the
outreach conducted during the
development of the proposed and final
MRR. Details of these meetings are
available in the docket (EPA–HQ–OAR–
2009–0926).
D. Unfunded Mandates Reform Act
(UMRA)
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), Pub. L.
104–4, establishes requirements for
Federal agencies to assess the effects of
their regulatory actions on State, local,
and tribal governments and the private
sector. Under Section 202 of the UMRA,
EPA generally must prepare a written
statement, including a cost-benefit
analysis, for final rules with ‘‘Federal
mandates’’ that may result in
expenditures to State, local, and tribal
governments, in the aggregate, or to the
private sector, of $100 million or more
in any one year.
This proposed rule does not contain
a Federal mandate that may result in
expenditures of $100 million or more
for State, local, and tribal governments,
in the aggregate, or the private sector in
any one year. Overall, EPA estimates
that the total annualized costs of this
proposed rule are approximately
$713,000 per year. Thus, this proposed
rule is not subject to the requirements
of sections 202 or 205 of UMRA.
This proposed rule is also not subject
to the requirements of section 203 of
UMRA because it contains no regulatory
requirements that might significantly or
uniquely affect small governments.
Facilities subject to the proposed rule
include facilities that inject CO2 for
enhanced recovery of crude oil, and
those intending to sequester CO2. None
of the facilities currently known to
undertake these activities are owned by
small governments.
E. Executive Order 13132: Federalism
This action does not have federalism
implications. It will not have substantial
direct effects on the States, on the
relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. This regulation
applies directly to facilities that inject
CO2 underground. Few, if any, State or
local government facilities would be
affected. This regulation also does not
limit the power of States or localities to
collect GHG data and/or regulate GHG
emissions. Thus, Executive Order 13132
does not apply to this action.
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In the spirit of Executive Order 13132,
and consistent with EPA policy to
promote communications between EPA
and State and local governments, EPA
specifically solicits comment on this
proposed action from State and local
officials.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (59 FR
22951, November 6, 2000), requires EPA
to develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’
This proposed rule is not expected to
have tribal implications, as specified in
Executive Order 13175. This regulation
applies to facilities that inject CO2
underground. Few facilities expected to
be affected by the rule are likely to be
owned by tribal governments. Thus,
Executive Order 13175 does not apply
to this proposed rule.
Although Executive Order 13175 does
not apply to this proposed rule, EPA
sought opportunities to provide
information to tribal governments and
representatives during development of
the MRR. In consultation with EPA’s
American Indian Environment Office,
EPA’s outreach plan included tribes.
During the proposal phase, EPA staff
provided information to tribes through
conference calls with multiple Indian
working groups and organizations at
EPA that interact with tribes and
through individual calls with two tribal
board members of TCR. In addition,
EPA prepared a short article on the GHG
reporting rule that appeared on the front
page of a tribal newsletter—Tribal Air
News—that was distributed to EPA/
Office of Air Quality Planning &
Standards’ network of tribal
organizations. EPA gave a presentation
on various climate efforts, including the
MRR, at the National Tribal Conference
on Environmental Management in June,
2008. In addition, EPA had copies of a
short information sheet distributed at a
meeting of the National Tribal Caucus.
EPA participated in a conference call
with tribal air coordinators in April
2009 and prepared a guidance sheet for
Tribal governments on the proposed
rule. It was posted on the MRR Web site
and published in the Tribal Air
Newsletter. For a complete list of tribal
contacts, see the ‘‘Summary of EPA
Outreach Activities for Developing the
Greenhouse Gas Reporting Rule,’’ in the
MRR Docket (EPA–HQ–OAR–2008–
0508–055). In addition to the
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consultation activities supporting the
MRR, EPA continues to provide
requested information to tribal
governments and representatives during
development of MRR source categories
that have not been finalized (Track II
rules) such as this proposed rulemaking.
EPA specifically solicits additional
comment on this proposed action from
tribal officials.
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
EPA interprets EO 13045 (62 FR
19885, April 23, 1997) as applying only
to those regulatory actions that concern
health or safety risks, such that the
analysis required under section 5–501 of
the EO has the potential to influence the
regulation. This proposed action is not
subject to EO 13045 because it does not
establish an environmental standard
intended to mitigate health or safety
risks.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This proposed rule is not a
‘‘significant energy action’’ as defined in
EO 13211 (66 FR 28355, May 22, 2001)
because it is not likely to have a
significant adverse effect on the supply,
distribution, or use of energy. Further,
EPA has concluded that this proposed
rule is not likely to have any adverse
energy effects. This proposed rule
relates to monitoring, reporting and
recordkeeping at facilities that inject
CO2 underground and does not impact
energy supply, distribution or use.
Therefore, EPA concludes that this
proposed rule is not likely to have any
adverse effects on energy supply,
distribution, or use.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (NTTAA), Public Law 104–
113 (15 U.S.C. 272 note) directs EPA to
use voluntary consensus standards in its
regulatory activities unless to do so
would be inconsistent with applicable
law or otherwise impractical. Voluntary
consensus standards are technical
standards (e.g., materials specifications,
test methods, sampling procedures, and
business practices) that are developed or
adopted by voluntary consensus
standards bodies. NTTAA directs EPA
to provide Congress, through OMB,
explanations when the Agency decides
not to use available and applicable
voluntary consensus standards.
This proposed rulemaking involves
technical standards. EPA will use
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18599
voluntary consensus standards from at
least seven different voluntary
consensus standards bodies, including
the following: American Society for
Testing and Materials (ASTM),
American Society of Mechanical
Engineers (ASME), International
Standards Organization (ISO), Gas
Processors Association, American Gas
Association, American Petroleum
Institute, and National Lime
Association. These voluntary consensus
standards will help facilities monitor,
report, and keep records of CO2
injections or geologic sequestration, and
any associated GHG emissions. No new
test methods were developed for this
proposed rule. Instead, from existing
rules for source categories and voluntary
greenhouse gas programs, EPA
identified existing means of monitoring,
reporting, and keeping records of
greenhouse gas emissions. The existing
methods (voluntary consensus
standards) include a broad range of
measurement techniques, such as
methods to measure gas or liquid flow;
and methods to gauge and measure
petroleum and petroleum products. The
test methods are incorporated by
reference into the proposed rule and are
available as specified in 40 CFR 98.7.
By incorporating voluntary consensus
standards into this proposed rule, EPA
is both meeting the requirements of the
NTTAA and presenting multiple
options and flexibility in complying
with the proposed rule. EPA welcomes
comments on this aspect of the
proposed rulemaking and, specifically,
invites the public to identify
potentially-applicable voluntary
consensus standards and to explain why
such standards should be used in this
proposed regulation.
J. Executive Order 12898: Federal
Actions to Address Environmental
Justice in Minority Populations and
Low-Income Populations
EO 12898 (59 FR 7629, February 16,
1994) establishes Federal executive
policy on environmental justice. Its
main provision directs Federal agencies,
to the greatest extent practicable and
permitted by law, to make
environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the United States.
EPA has determined that this
proposed rule will not have
disproportionately high and adverse
human health or environmental effects
on minority or low-income populations
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because it does not affect the level of
protection provided to human health or
the environment. This proposed rule
does not affect the level of protection
provided to human health or the
environment because it is a rule
addressing information collection and
reporting procedures.
Guam, and any other Commonwealth,
territory or possession of the United
States, as well as the territorial sea as
defined by Presidential Proclamation
No. 5928.
*
*
*
*
*
4. Section 98.7 is amended by revising
paragraph (e)(39) to read as follows:
List of Subjects in 40 CFR Part 98
Environmental protection,
Administrative practice and procedure,
Greenhouse gases, Incorporation by
reference, Air pollution control,
Reporting and recordkeeping
requirements.
§ 98.7 What standardized methods are
incorporated by reference into this part?
Dated: March 22, 2010.
Lisa P. Jackson,
Administrator.
For the reasons stated in the
preamble, title 40, chapter I, of the Code
of Federal Regulations is proposed to be
amended as follows:
PART 98—[AMENDED]
1. The authority citation for part 98
continues to read as follows:
Authority: 42 U.S.C. 7401, et seq.
Subpart A—[Amended]
2. Section 98.2 is amended by revising
paragraph (a) introductory text to read
as follows:
§ 98.2
Who must report?
(a) The GHG reporting requirements
and related monitoring, recordkeeping,
and reporting requirements of this part
apply to the owners and operators of
any facility that is located in the United
States or under or attached to the Outer
Continental Shelf (as defined in 43
U.S.C. 1331) and that meets the
requirements of either paragraph (a)(1),
(a)(2), or (a)(3) of this section; and any
supplier that meets the requirements of
paragraph (a)(4) of this section:
*
*
*
*
*
3. Section 98.6 is amended by adding
the following definitions in alphabetical
order to read as follows:
§ 98.6
Definitions.
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*
*
*
*
*
Outer Continental Shelf means all
submerged lands lying seaward and
outside of the area of lands beneath
navigable waters as defined in 43 U.S.C.
1301, and of which the subsoil and
seabed appertain to the United States
and are subject to its jurisdiction and
control.
*
*
*
*
*
United States means the 50 States, the
District of Columbia, the
Commonwealth of Puerto Rico,
American Samoa, the Virgin Islands,
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*
*
*
*
*
(e) * * *
(39) ASTM E1747–95 (Reapproved
2005) Standard Guide for Purity of
Carbon Dioxide Used in Supercritical
Fluid Applications, IBR approved for
§ 98.424(b) and § 98.444(a).
*
*
*
*
*
5. Part 98 is amended by adding
subpart RR to read as follows:
Sec.
98.440 Definition of the source category.
98.441 Reporting threshold.
98.442 GHGs to report.
98.443 Calculating CO2 Injection and
Sequestration.
98.444 Monitoring and QA/QC
requirements.
98.445 Procedures for estimating missing
data.
98.446 Data reporting requirements.
98.447 Records that must be retained.
98.448 Geologic Sequestration Monitoring,
Reporting, and Verification (MRV) Plan.
98.449 Definitions.
Subpart RR—Injection and Geologic
Sequestration of Carbon Dioxide
§ 98.440
Definition of the source category.
(a) The injection and geologic
sequestration of carbon dioxide (CO2)
source category comprises any well or
group of wells that inject CO2 into the
subsurface, which includes under a
seabed offshore. The source category
consists of all wells that inject CO2 into
the subsurface, including wells for
geologic sequestration (GS) or for any
other purpose.
(b) A facility that is subject to this rule
only because of CO2 injection wells that
do not meet the definition of geologic
sequestration facility in paragraph (c) of
this section is not required to report
emissions under any other subpart of
part 98.
(c) Geologic sequestration (GS)
facility.
(1) For the purposes of this source
category, a geologic sequestration
facility is a facility that injects CO2 for
the long-term containment of a gaseous,
liquid, or supercritical CO2 stream in
subsurface geologic formations. A
facility that injects CO2 to enhance the
recovery of oil or natural gas is not a
geologic sequestration facility for the
purposes of this source category unless
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the facility also injects the CO2 in
subsurface geologic formations for longterm containment of a gaseous, liquid,
or supercritical CO2 stream and chooses
to submit a monitoring, reporting, and
verification (MRV) plan to EPA that is
then approved by EPA.
(2) A facility that is not required to
report for the purposes of this source
category as a geologic sequestration
facility, injects CO2 for the long-term
containment of a gaseous, liquid, or
supercritical CO2 stream in subsurface
geologic formations, and chooses to
submit an MRV plan to EPA that is then
approved by EPA, is a geologic
sequestration facility.
(3) A geologic sequestration facility
includes all structures associated with
injection located between the points of
CO2 transfer onsite and the injection
wells.
(4) A geologic sequestration facility
that injects CO2 to enhance the recovery
of oil or natural gas includes all
structures associated with production
located between the production wells
and the separators.
(d) This source category does not
include the following:
(1) Storage of CO2 above ground.
(2) Temporary storage of CO2 below
ground.
(3) Transportation or distribution of
CO2.
(4) Purification, compression, or
processing of CO2 at the surface.
(5) Capture of CO2.
(6) CO2 in cement, precipitated
calcium carbonate (PCC), or any other
technique that does not involve
injection of CO2 into the subsurface.
§ 98.441
Reporting threshold.
(a) You must report under this subpart
if your facility is an injection facility
that injects CO2 into the subsurface and
the facility meets requirements of either
§ 98.2(a)(1) or (a)(2).
(b) The requirements of § 98.2(i) do
not apply to this subpart. Once a facility
is subject to the requirements of this
subpart, the owner or operator must
continue for each year thereafter to
comply with all requirements of this
subpart, including the requirement to
submit annual GHG reports, even if the
facility does not meet the applicability
requirements in paragraph (a) of
§ 98.2(a) of this part in a future year,
unless paragraphs (b)(1) or (b)(2) of this
section apply.
(1) If the injection well or wells
constituting the facility are plugged in
compliance with the facility’s
Underground Injection Control permit
requirements (or relevant permit
requirements, if any, in the case of a
facility that is not under the jurisdiction
E:\FR\FM\12APP2.SGM
12APP2
Federal Register / Vol. 75, No. 69 / Monday, April 12, 2010 / Proposed Rules
requirements, if any, in the case of a
facility that is not under the jurisdiction
of the Safe Drinking Water Act), a
facility conducting geologic
sequestration may discontinue
complying with the remainder of this
subpart. The owner or operator of the
facility must notify EPA that the CO2
plume and pressure front have
stabilized and the GS facility has been
closed in compliance with the facility’s
Underground Injection Control permit
requirements (or relevant permit
requirements, if any, in the case of a
facility that is not under the jurisdiction
of the Safe Drinking Water Act), and
such notification must be certified as
accurate by the owner or operator of the
facility. The owner or operator must
resume reporting for any future calendar
year during which any activities that are
source categories of this subpart resume
operation.
§ 98.442
CO 2, v =
VerDate Nov<24>2008
17:10 Apr 09, 2010
Jkt 220001
∑ Q p,v ∗ CCO2, p,v
(Eq. RR-1)
p =1
(2) For each transfer point for which
flow is measured using a volumetric
flow meter, you must calculate the total
annual mass of CO2 in a CO2 stream
transferred onsite from offsite sources in
metric tons by multiplying the
4
∑ Q p,v ∗ D p,v ∗ CCO2, p,v
(Eq. RR- 2)
p =1
(3) To aggregate transfer data at the
facility level, you must sum the mass of
all CO2 transferred onsite from offsite
sources through all facility transfer
points in accordance with the procedure
specified in Equation RR–3 of this
section.
V
CO 2T = ∑ CO 2,v
(Eq. RR-3)
v =1
Where:
PO 00000
volumetric flow at standard conditions
by the CO2 concentration in the flow
and the density of CO2 at standard
conditions, according to Equation RR–2
of this section. You must collect these
data quarterly. Volumetric flow and
concentration data measurements must
be made in accordance with § 98.444.
Frm 00027
Fmt 4701
Sfmt 4702
CO2T = Total annual CO2 mass transferred
onsite from offsite sources (metric tons)
through all transfer points at the facility.
CO2,v = Annual CO2 mass transferred (metric
tons) through transfer point v.
v = transfer point.
(b) A facility must report annually the
mass of CO2 injected in accordance with
the procedures specified in paragraphs
(b)(1) through (b)(3) of this section.
(1) For each point at which the flow
of an injected CO2 stream is measured
using a mass flow meter, you must
calculate annually the total mass of CO2
in the CO2 stream injected in metric
E:\FR\FM\12APP2.SGM
12APP2
EP12AP10.027
mstockstill on DSKH9S0YB1PROD with PROPOSALS2
Where:
CO2,v = Annual CO2 mass transferred onsite
from offsite sources (metric tons) through
transfer point v.
Qp,v = Quarterly volumetric flow rate
measurement for transfer point v in quarter
p at standard conditions (standard cubic
meters per quarter).
Dp,v = Density of CO2 at standard
conditions (metric tons per standard cubic
meter): 0.0018704.
CCO2,p,v = Quarterly CO2 concentration
measurement in flow for transfer point v in
quarter p (wt. %CO2/100).
p = quarter.
v = transfer point.
(a) A facility must calculate and
report the annual mass of CO2
transferred to the facility from offsite
sources using the procedures in
paragraphs (a)(1), (a)(2), and (a)(3) of
this section.
(1) For each transfer point for which
flow is measured using a mass flow
meter, you must calculate the total
annual mass of CO2 in a CO2 stream
transferred onsite from offsite sources in
metric tons by multiplying the mass
flow by the CO2 concentration in the
flow, according to Equation RR–1 of this
section. You must collect these data
quarterly. Mass flow and concentration
data measurements must be made in
accordance with § 98.444.
4
p = quarter.
v = transfer point.
CO 2, v =
§ 98.443 Calculating CO2 Injection and
Sequestration.
EP12AP10.026
Where:
CO2,v = Annual CO2 mass transferred onsite
from offsite sources (metric tons) through
transfer point v.
Qp,v = Quarterly mass flow rate measurement
for transfer point v in quarter p (metric
tons per quarter).
CCO2,p,v = Quarterly CO2 concentration
measurement in flow for transfer point v
in quarter p (wt. %CO2/100).
GHGs to report.
You must report:
(a) Mass of CO2 received onsite.
(b) Mass of CO2 injected into the
subsurface.
(c) Facilities conducting geologic
sequestration also report:
(1) Mass of CO2 produced, if any.
(2) Mass of CO2 sequestered in the
subsurface geologic formation.
(3) Mass of CO2 emitted from
subsurface leaks.
(4) Mass of fugitive and vented CO2
emissions from surface equipment at the
facility if not reported under subpart W
of this part.
EP12AP10.025
of the Safe Drinking Water Act), a
facility conducting geologic
sequestration subject to the
requirements of this subpart may
discontinue complying with § 98.442(a)
and § 98.442(b) and all other facilities
subject to the requirements of this
subpart may discontinue complying
with this subpart. The owner or operator
of the facility must notify EPA that the
injection well or wells constituting the
facility have been plugged in
compliance with the facility’s
Underground Injection Control permit
requirements (or relevant permit
requirements, if any, in the case of a
facility that is not under the jurisdiction
of the Safe Drinking Water Act), and
such notification must be certified as
accurate by the owner or operator of the
facility. The owner or operator must
resume reporting for any future calendar
year during which any activities that are
source categories of this subpart resume
operation.
(2) If the CO2 plume and pressure
front have stabilized and the GS facility
has been closed in compliance with the
facility’s Underground Injection Control
permit requirements (or relevant permit
18601
18602
Federal Register / Vol. 75, No. 69 / Monday, April 12, 2010 / Proposed Rules
section. You must collect these data
quarterly. Mass flow and concentration
CO 2,u =
(2) For each point at which the flow
of an injected CO2 stream is measured
using a volumetric flow meter, you must
calculate annually the total mass of CO2
in the CO2 stream injected in metric
tons by multiplying the volumetric flow
(Eq. RR-6)
u =1
Where:
4
∑ Q p,u ∗ D p,u ∗ CCO2, p,u
CO2I = Total annual CO2 mass injected
(metric tons) through all injection wells.
CO2,u = Annual CO2 mass injected (metric
tons) as measured by flow meter u.
u = flow meter.
(c) All GS facilities must also report
the mass of CO2 emitted as fugitive or
vented emissions from surface
equipment (if this information is not
required to be reported under subpart W
of this part), the mass of CO2 produced
(if applicable), the mass of CO2 emitted
from subsurface leakage, and the mass
of CO2 geologically sequestered in
accordance with the procedures as
specified in paragraphs (c)(1) through
(c)(4) of this section.
(1) If you do not report CO2 emitted
as fugitive or vented emissions from
surface equipment at your facility in the
reporting year under subpart W of this
part, you must report them under
subpart RR of this part in accordance
with the procedures specified in subpart
W of this part for each type of surface
mstockstill on DSKH9S0YB1PROD with PROPOSALS2
CO 2, w =
Where:
CO2,w = Annual CO2 mass produced (metric
tons) through separator w.
Qp,w = Quarterly mass flow rate measurement
for separator w in quarter p (metric tons
per quarter).
CCO2,p,w = Quarterly CO2 concentration
measurement in flow for separator w in
quarter p (wt. % CO2/100).
VerDate Nov<24>2008
17:10 Apr 09, 2010
Jkt 220001
(Eq. RR-5)
p =1
4
∑ Q p,w ∗ CCO 2, p,w
(Eq. RR-7)
p =1
p = quarter.
w = separator.
(ii) For each gas-liquid separator for
which flow is measured using a
volumetric flow meter, you must
calculate annually the total mass of CO2
produced from an oil or gas stream in
metric tons by multiplying the
PO 00000
equipment. If you report these
emissions under subpart W of this part,
you do not need to report these
emissions under subpart RR of this part.
(2) You must calculate the annual
mass of CO2 produced from oil or gas
production wells (if applicable) at the
facility for each separator that sends a
stream of gas into a recycle or end use
system in accordance with the
procedures specified in paragraphs
(c)(2)(i) through (c)(2)(iii) of this section.
(i) For each gas-liquid separator for
which flow is measured using a mass
flow meter, you must calculate annually
the total mass of CO2 produced from an
oil or gas stream in metric tons by
multiplying the mass flow by the CO2
concentration in the flow, according to
Equation RR–7 of this section. You must
collect these data quarterly. Mass flow
and concentration data measurements
must be made in accordance with
§ 98.444.
EP12AP10.031
U
CO2 I = ∑ CO2,u
at standard conditions by the CO2
concentration in the flow and the
density of CO2 at standard conditions,
according to Equation RR–5 of this
section. You must collect these data
quarterly. Volumetric flow and
concentration data measurements must
be made in accordance with § 98.444.
Frm 00028
Fmt 4701
Sfmt 4702
volumetric flow at standard conditions
by the CO2 concentration in the flow
and the density of CO2 at standard
conditions, according to Equation RR–8
of this section. You must collect these
data quarterly. Volumetric flow and
concentration data measurements must
be made in accordance with § 98.444.
E:\FR\FM\12APP2.SGM
12APP2
EP12AP10.030
(3) To aggregate injection data at the
facility level, you must sum the mass of
all CO2 injected through all injection
wells at the facility in accordance with
the procedure specified in Equation RR–
6 of this section.
(Eq. RR- 4)
p =1
p = quarter.
u = flow meter.
CO 2,u =
Where:
CO2,u = Annual CO2 mass injected (metric
tons) as measured by flow meter u.
Qp,u = Quarterly volumetric flow rate
measurement for flow meter u in quarter
p at standard conditions (standard cubic
meters per quarter).
Dp,u = Density of CO2 at standard conditions
(metric tons per standard cubic meter):
0.0018704.
CCO2,p,u = CO2 concentration measurement in
flow for transfer point u in quarter p (wt.
%CO2/100).
p = quarter.
u = flow meter.
4
∑ Q p,u ∗ CCO2, p,u
EP12AP10.029
Where:
CO2,u = Annual CO2 mass injected (metric
tons) as measured by flow meter u.
Qp,u = Quarterly mass flow rate measurement
for flow meter u in quarter p (metric tons
per quarter).
CCO2,p,u = Quarterly CO2 concentration
measurement in flow in quarter p (wt.
%CO2/100).
data measurements must be made in
accordance with § 98.444.
EP12AP10.028
tons by multiplying the mass flow by
the CO2 concentration in the flow,
according to Equation RR–4 of this
Federal Register / Vol. 75, No. 69 / Monday, April 12, 2010 / Proposed Rules
CO 2, w =
Where:
CO2,w = Annual CO2 mass produced (metric
tons) through separator w.
Qp,w = Volumetric flow rate measurement for
separator w in quarter p at standard
conditions (standard cubic meters per
quarter).
Dp,w = Density of CO2 at standard conditions
(metric tons per standard cubic meter):
0.0018704.
18603
4
∑ Q p,w ∗ D p,w ∗ CCO 2, p,w
(Eq. RR-8)
p =1
CCO2,p,w = CO2 concentration measurement in
flow for separator w in quarter p (wt. %
CO2/100).
p = quarter.
w = separator.
(iii) To aggregate production data at
the facility level, you must sum the
mass of all of the CO2 separated at each
gas-liquid separator at the facility in
accordance with the procedure specified
in Equation RR–9 of this section. You
must assume that the total CO2
measured at the separator(s) represents
(100–X)% of the total CO2 produced. In
order to account for the X% of CO2
produced that is estimated to remain
with the produced oil and gas, you must
multiply the quarterly mass of CO2
measured at the separator(s) by
(100+X)%. The value of X must be
estimated using a methodology
approved by EPA per your MRV plan.
W
CO 2 P = (100 + X)% ∗ ∑ CO 2,w
(Eq. RR-9)
w=1
pathways at the facility in accordance
with the procedure specified in
Equation RR–10 of this section.
X
(Eq. RR-10)
x =1
Where:
CO2E = Total annual CO2 mass emitted from
the subsurface geologic formation (metric
tons) at the facility in the reporting year.
CO2,x = Annual CO2 mass emitted (metric
tons) at leakage pathway x in the
reporting year.
x = leakage pathway.
CO2E = Total annual CO2 mass emitted
(metric tons) from the subsurface
geologic formation in the reporting year.
CO2FI = Total annual CO2 mass emitted
(metric tons) as fugitive or vented
emissions from equipment located on the
surface between the flow meter used to
measure injection quantity and the
injection wellhead.
CO2FP = Total annual CO2 mass emitted
(metric tons) as fugitive or vented
emissions from equipment located on the
mstockstill on DSKH9S0YB1PROD with PROPOSALS2
CO2 = CO2 I − CO2 E − CO2 FI
Where:
CO2 = Total annual CO2 mass sequestered in
the subsurface geologic formation (metric
tons) at the facility in the reporting year.
CO2I = Total annual CO2 mass injected
(metric tons) at the facility in the
reporting year.
VerDate Nov<24>2008
17:10 Apr 09, 2010
Jkt 220001
Frm 00029
Fmt 4701
Sfmt 4702
(ii) GS facilities that are not actively
producing oil or natural gas must
calculate the annual mass of CO2 that is
sequestered in the subsurface geologic
formation in the reporting year in
accordance with the procedures
specified in Equation RR–12 of this
section.
(Eq. RR-12)
CO2E = Total annual CO2 mass emitted
(metric tons) from the subsurface
geologic formation in the reporting year.
CO2FI = Total annual CO2 mass emitted
(metric tons) as fugitive or vented
emissions from equipment located on the
surface between the flow meter used to
measure injection quantity and the
injection wellhead.
PO 00000
surface between the production wellhead
and of the flow meter used to measure
production quantity.
§ 98.444 Monitoring and QA/QC
requirements.
(a) All reporters must adhere to the
requirements and procedures in
paragraph (a) in this section if there has
been no EPA direction or order
specifying a preferred method of
measurement.
E:\FR\FM\12APP2.SGM
12APP2
EP12AP10.036
Where:
CO2 = Total annual CO2 mass sequestered in
the subsurface geologic formation (metric
tons) at the facility in the reporting year.
CO2I = Total annual CO2 mass injected
(metric tons) at the facility in the
reporting year.
CO2P = Total annual CO2 mass produced
(metric tons) at the facility in the
reporting year.
(Eq. RR-11)
EP12AP10.035
CO2 = CO2 I − CO2 P − CO2 E − CO2 FI − CO2 FP
EP12AP10.034
(3) You must report the annual mass
of CO2 that is emitted from each leakage
pathway identified in your MRV plan.
You must calculate the total annual
mass of CO2 emitted from all leakage
EP12AP10.033
CO 2 E = ∑ CO 2,x
(4) You must report the annual mass
of CO2 that is sequestered in the
subsurface geologic formation in the
reporting year in accordance with the
procedures specified in paragraphs
(c)(4)(i) and (c)(4)(ii) of this section.
(i) GS facilities that are conducting
enhanced recovery operations and that
are actively producing oil or natural gas
must calculate the annual mass of CO2
that is sequestered in the underground
subsurface formation in the reporting
year in accordance with the procedure
specified in Equation RR–11 of this
section.
EP12AP10.032
Where:
CO2P = Total annual CO2 mass produced
(metric tons) through all separators in
the reporting year.
CO2,w = Annual CO2 mass produced (metric
tons) through separator w in the
reporting year.
X = Percent of CO2 that is estimated to
remain with the produced oil and gas.
w = separator.
mstockstill on DSKH9S0YB1PROD with PROPOSALS2
18604
Federal Register / Vol. 75, No. 69 / Monday, April 12, 2010 / Proposed Rules
(1) You must determine the quantity
transferred by following the most
appropriate of the following procedures:
(i) A reporter can measure quantity at
the custody transfer meter installed at
the facility boundary prior to any
subsequent processing operations at the
facility.
(ii) If you took ownership of the CO2
in a commercial transaction, you can
use the quantity data from the sales
contract if it is a one-time transaction or
from invoices or manifests if it is an
ongoing commercial transaction with
discrete shipments.
(2) The point of measurement for the
quantity injected is specified in
paragraphs (a)(2)(i) and (a)(2)(ii) of this
section.
(i) For facilities regulated by the
Underground Injection Control program,
the point of measurement is the flow
meter installed at the facility you
already use to comply with the flow
monitoring and reporting provisions of
your Underground Injection Control
permit.
(ii) For facilities not regulated by the
Underground Injection Control program
because they are outside of Safe
Drinking Water Act jurisdiction, the
point of measurement is the flow meter
installed at the facility you already use
to comply with the flow monitoring and
reporting provisions of your relevant
permit. If no such requirement exists,
the point of measurement is the flow
meter installed closest to the point of
injection at your facility.
(3) You must determine the quantity
injected by using a flow meter or meters.
(4) You must operate and calibrate all
flow meters used to measure quantities
reported in § 98.443 according to the
following procedure:
(i) You must use an appropriate
standard method published by a
consensus-based standards organization
if such a method exists. Consensusbased standards organizations include,
but are not limited to, the following:
ASTM International, the American
National Standards Institute (ANSI), the
American Gas Association (AGA), the
American Society of Mechanical
Engineers (ASME), the American
Petroleum Institute (API), and the North
American Energy Standards Board
(NAESB).
(ii) Where no appropriate standard
method developed by a consensus-based
standards organization exists, you must
follow industry standard practices.
(iii) You must ensure that any flow
meter calibrations performed are NIST
traceable.
(5) You must determine concentration
of the transferred CO2 stream by
VerDate Nov<24>2008
17:10 Apr 09, 2010
Jkt 220001
following the most appropriate of the
following procedures:
(i) A reporter can sample the CO2
stream at the point of transfer and
measure its concentration.
(ii) If you took ownership of the CO2
in a commercial transaction for which
the sales contract was contingent on
CO2 concentration, and if the supplier of
the CO2 sampled the CO2 stream and
measured its concentration per the sales
contract terms, you can use the CO2
concentration data from the sales
contract.
(6) You must determine the CO2
concentration of the injected CO2 stream
by measuring immediately downstream
of the flow meter as specified in
paragraph (a)(2)(i) or (a)(2)(ii) of this
section.
(7) If you measure the concentration
of any CO2 quantity for reporting, you
must use methods that conform to
applicable chemical analytical
standards. Acceptable methods include
U.S. Food and Drug Administration
food-grade specifications for CO2 (see 21
CFR 184.1240) and ASTM standard
E1747–95 (Reapproved 2005) Standard
Guide for Purity of Carbon Dioxide Used
in Supercritical Fluid Applications
(incorporated by reference, see § 98.7).
(8) You must determine the
transferred CO2 concentration and flow
quarterly.
(9) You must sample the injected CO2
concentration and calculate the flow
quarterly.
(10) You must use the same
calculation methodology throughout a
reporting period unless you provide a
written explanation of why a change in
methodology was required.
(11) If you measure the flow of the
CO2 transferred or injected with a
volumetric flow meter, you shall
convert all measured volumes of carbon
dioxide to the following standard
industry temperature and pressure
conditions for use in equations RR–2
and RR–5: Standard cubic meters at a
temperature of 60 degrees Fahrenheit
and at an absolute pressure of 1
atmosphere.
(b) GS facilities must additionally
submit an MRV plan to EPA, receive
approval from EPA, and adhere to the
requirements and procedures in
paragraph (b) of this section.
(1) You must adhere to paragraphs
(a)(1) through (a)(11) of this section.
(2) For reporters who are not required
to report the quantity of CO2 emitted as
fugitive or vented emissions from
surface equipment at the injection site
under subpart W of this part, and are
thereby required to report fugitive and
vented emissions from surface
equipment under this subpart,
PO 00000
Frm 00030
Fmt 4701
Sfmt 4702
monitoring and QA/QC requirements for
these data should be followed in
accordance with procedures specified in
subpart W of this part.
(3) The point of measurement for the
quantity of CO2 produced from oil or
natural gas production wells at the GS
facility is a flow meter directly
downstream of each separator that sends
a stream of gas into a recycle or end use
system.
(4) The point of measurement for the
concentration of the stream of CO2
produced is directly downstream of
each separator that sends a stream of gas
into a recycle or end use system.
(5) You must sample the produced
CO2 concentration and flow quarterly.
(6) A reporter must follow the
procedures outlined in the most recent
MRV plan submitted to and approved
by EPA to determine the quantity of CO2
emitted from the subsurface geologic
formation and the percent of CO2 that is
estimated to remain with the produced
oil and natural gas.
(c) For 2011, a facility that is subject
to this rule only because of a CO2
injection well(s) that does not meet the
definition of GS facility in § 98.440(c)
may follow the provisions of § 98.3(d)(1)
through (3) for best available monitoring
methods rather than follow the
monitoring requirements of this section.
For purposes of this subpart, any
reference to the year 2010 in § 98.3(d)(1)
through (3) shall mean 2011.
(d) All flow meters must be operated
continuously.
(e) If you measure the flow of the CO2
produced with a volumetric flow meter,
you shall convert all measured volumes
of carbon dioxide to the following
standard industry temperature and
pressure conditions for use in equation
RR–8: Standard cubic meters at a
temperature of 60 degrees Fahrenheit
and at an absolute pressure of 1
atmosphere.
§ 98.445 Procedures for estimating
missing data.
(a) A complete record of all measured
parameters used in the GHG quantities
calculations is required. Whenever the
quality assurance procedures for all
facilities covered under this subpart
cannot be followed to measure flow and
concentration, the most appropriate of
the following missing data procedures
must be followed if EPA has not
specified a preferred procedure:
(1) A quarterly quantity of CO2
injected that is missing must be
estimated using the quantity of CO2
injected from the nearest previous
period of time at a similar injection
pressure.
E:\FR\FM\12APP2.SGM
12APP2
Federal Register / Vol. 75, No. 69 / Monday, April 12, 2010 / Proposed Rules
(2) A quarterly quantity of new CO2
transferred onto the facility from offsite
that is missing must be estimated using
the quantity of new CO2 flow based on
supplier data or supplier-operated flow
meters.
(3) A quarterly concentration value
that is missing must be estimated using
a concentration value from the nearest
previous time period.
(b) A complete record of all measured
parameters used in the GHG quantities
calculations is required. Whenever the
quality assurance procedures for
facilities conducting GS cannot be
followed, the most appropriate of the
following missing data procedures must
be followed:
(1) For any values associated with
fugitive or vented CO2 emissions from
surface equipment at the facility that are
reported in this supbart, missing data
estimation procedures should be
followed in accordance with those
specified in subpart W of this part.
(2) The annual quantity of CO2
produced from the subsurface geologic
formation that is missing must be
estimated according to the following:
(i) If an applicable procedure was
included in the reporter’s MRV plan
submitted to EPA, that procedure must
be applied.
(ii) If the procedure included in the
reporter’s MRV plan is not applicable,
or if the reporter did not include a
procedure in the MRV plan, the reporter
must estimate annual quantity of CO2
produced by subtracting the annual
quantity of CO2 transferred onsite from
offsite from the annual quantity of CO2
injected.
(3) The annual quantity of CO2
emitted from the subsurface geologic
formation must be estimated following
the procedure included in the reporter’s
MRV plan submitted to EPA.
(4) All other missing data procedures
as outlined in your approved MRV plan
must be followed.
mstockstill on DSKH9S0YB1PROD with PROPOSALS2
§ 98.446
Data reporting requirements.
In addition to the information
required by § 98.3(c), report the
information listed in this section.
Facilities that are subject to this rule
only because of CO2 injection wells and
that do not meet the definition of GS
facility in § 98.440(c) do not report the
information in § 98.3(c)(4).
(a) For each transfer point flow meter
(mass or volumetric), report:
(1) CO2 quantity transferred onsite
(metric tons or standard cubic meters, as
appropriate) in each quarter.
(2) CO2 concentration in flow (volume
or wt. % CO2/100) in each quarter.
(3) If a volumetric flow meter is used,
volumetric flow rate at standard
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17:10 Apr 09, 2010
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conditions (standard cubic meters) in
each quarter.
(4) If a mass flow meter is used, mass
flow rate (metric tons) in each quarter.
(5) The standard used to calculate
each value in paragraphs (a)(1) through
(a)(4) of this section.
(6) The number of times in the
reporting year for which substitute data
procedures were used to calculate
values reported in paragraphs (a)(1)
through (a)(4) of this section.
(b) For each injection flow meter
(mass or volumetric), report:
(1) CO2 quantity injected (metric tons
or standard cubic meters) in each
quarter.
(2) CO2 concentration in flow (volume
or wt. % CO2/100) in each quarter.
(3) If a volumetric flow meter is used,
volumetric flow rate at standard
conditions (standard cubic meters) in
each quarter.
(4) If a mass flow meter is used, mass
flow rate (metric tons) in each quarter.
(5) The standard used to calculate
each value in paragraphs (b)(1) through
(b)(4) of this section.
(6) The number of times in the
reporting year for which substitute data
procedures were used to calculate
values reported in paragraphs (b)(1)
through (b)(4) of this section.
(c) The source of the supplied CO2, if
known, according to the following
categories:
(1) CO2 production wells.
(2) Electric generating unit.
(3) Ethanol plant.
(4) Pulp and paper mill.
(5) Natural gas processing.
(6) Other anthropogenic source.
(7) Unknown.
(d) The total CO2 received onsite
(metric tons) in the reporting year as
calculated in Equation RR–3.
(e) The total CO2 injected (metric
tons) in the reporting year as calculated
in Equation RR–6.
(f) GS facilities must also report the
following information:
(1) If you do not report under subpart
W of this part, report the annual fugitive
and vented CO2 emissions from surface
equipment (metric tons) located in the
GS facility under this subpart.
(2) Annual CO2 mass emitted (metric
tons) as fugitive or vented emissions
from equipment located on the surface
between the flow meter used to measure
injection quantity and the injection
wellhead.
(3) Annual CO2 mass emitted (metric
tons) as fugitive or vented emissions
from equipment located on the surface
between the production wellhead and of
the flow meter used to measure
production quantity.
(4) For each separator flow meter
(mass or volumetric), report:
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Fmt 4701
Sfmt 4702
18605
(i) CO2 quantity produced (metric tons
or standard cubic meters) in each
quarter.
(ii) CO2 concentration in flow (volume
or wt. % CO2/100) in each quarter.
(5) For each separator volumetric flow
meter, volumetric flow rate at standard
conditions (standard cubic meters) in
each quarter.
(6) For each separator mass flow
meter, mass flow rate (metric tons) in
each quarter.
(7) The standard used to calculate
each value in paragraphs (f)(4) through
(f)(6) of this section.
(8) The number of times in the
reporting year for which substitute data
procedures were used to calculate
values reported in paragraphs (f)(4)
through (f)(6) of this section.
(9) The value for X (%) used in
Equation RR–9 and as determined in
your MRV plan.
(10) Annual CO2 produced in the
reporting year as calculated in Equation
RR–9.
(11) For each leakage pathway, report
the CO2 (metric tons) emitted through
that pathway in the reporting year.
(12) Annual CO2 mass emitted (metric
tons) from the subsurface geologic
formation at the facility in the reporting
year as calculated by Equation RR–10.
(13) Annual CO2 (metric tons)
sequestered in the subsurface geologic
formation in the reporting year as
calculated by Equation RR–11 or RR–12.
(14) Cumulative mass of CO2 reported
as sequestered in the subsurface
geologic formation in all years since you
began reporting.
(15) Date that the most recent MRV
plan was approved and the MRV plan
approval number that was issued by
EPA.
(16) Whether any of the MRV plan
resubmissions scenarios were triggered
in the reporting year such that you must
submit a new MRV plan in the
following year.
(17) If the well is permitted by an
Underground Injection Control
permitting authority, for each injection
well, report:
(i) The well ID number used for the
Underground Injection Control permit.
(ii) The Underground Injection
Control permit class.
(18) Any other reporting requirement
that is specified in your MRV plan.
§ 98.447
Records that must be retained.
In addition to the records required by
§ 98.3(g), you must retain the records
specified in paragraphs (a) through (c) of
this section, as applicable.
(a) You must retain quarterly records
of injected CO2 and CO2 transferred onto
the facility from offsite sources,
E:\FR\FM\12APP2.SGM
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Federal Register / Vol. 75, No. 69 / Monday, April 12, 2010 / Proposed Rules
including mass flow or volumetric flow
at standard conditions and operating
conditions, operating temperature and
pressure, and concentration of these
streams.
(b) GS facilities must retain:
(1) Quarterly records of produced
CO2, if applicable, including mass flow
or volumetric flow at standard
conditions and operating conditions,
operating temperature and pressure, and
concentration of these streams.
(2) Annual records of the emitted CO2
from subsurface geologic formation
leakage pathways.
(3) Any other records as outlined for
retention in your MRV plan.
§ 98.448 Geologic Sequestration
Monitoring, Reporting, and Verification
(MRV) Plan.
mstockstill on DSKH9S0YB1PROD with PROPOSALS2
(a) A GS facility as defined in
§ 98.440(c) of this subpart must follow
the procedures outlined in this section
to develop a monitoring, reporting, and
verification (MRV) plan, submit it to
EPA, receive approval from EPA on the
plan, implement the plan, and submit
annual report addenda.
(1) You must develop an MRV plan
that contains the following components.
(i) An assessment of the risk of
leakage of CO2 to the surface.
(ii) A strategy for detecting and
quantifying any CO2 leakage to the
surface.
(iii) A strategy for establishing preinjection environmental baselines.
(iv) Summary of considerations made
to calculate site-specific variables for
the mass balance equation.
(2) A facility that injects CO2 to
enhance the recovery of oil or natural
gas or a facility that is not required to
report as a GS facility can voluntarily
submit the MRV plan to EPA at any
time.
(3) A GS facility that does not inject
CO2 to enhance the recovery of oil or
natural gas must submit the MRV plan
on the following schedule.
(i) A GS facility must submit the MRV
plan to EPA (A) within six months from
the time the facility’s Underground
Injection Control permitting authority
(or relevant permitting authority in the
case of a facility that is not under the
jurisdiction of the Safe Drinking Water
Act) confirms the area of review or (B)
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17:10 Apr 09, 2010
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by December 31 of the year that that the
Underground Injection Control
permitting authority (or relevant
permitting authority in the case of a
facility that is not under the jurisdiction
of the Safe Drinking Water Act)
confirms the area of review, whichever
date is later. A facility will be allowed
to request one extension of up to an
additional six months.
(ii) If the GS facility holds an
Underground Injection Control permit
(or relevant permit in the case of a
facility that is not under the jurisdiction
of the Safe Drinking Water Act) as of the
date of publication of this subpart or if
the Underground Injection Control
permitting authority (or relevant
permitting authority in the case of a
facility that is not under the jurisdiction
of the Safe Drinking Water Act) has
confirmed the area of review as of the
date of publication of this subpart, such
facility must submit the MRV plan to
EPA within six months of the date of
publication of this subpart. A facility
will be allowed to request one extension
of up to an additional six months.
(4) If you are using an Underground
Injection Control Class VI permit to
demonstrate that MRV plan
requirements have been satisfied and
the Underground Injection Control Class
VI permit has not been approved, you
must submit the identification number
associated with the Underground
Injection Control Class VI permit
application and notify EPA when the
Underground Injection Control Class VI
permit has been approved.
(5) Upon MRV plan submission, the
following approval process will apply.
(i) On a case-by-case basis, EPA will
determine if the submitted MRV plan is
complete, and evaluate the MRV plan to
ensure that the facility has an
appropriate strategy in place to
effectively quantify geologically
sequestered CO2.
(ii) You must implement the EPAapproved MRV plan once the plan is
final, regardless of the point in the
reporting year.
(6) If adjustments to the MRV plan are
made due to new information or altered
site conditions or if a leak is detected in
a calendar year, you must submit an
addendum at the same time as the next
annual report (March 31 of the
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Fmt 4701
Sfmt 9990
subsequent calendar year) that includes
the following components.
(i) A description of the leak including
all assumptions, methodology, and
technologies involved in leakage
detection and quantification, if a leak
was detected.
(ii) A description of how the
monitoring strategy was adjusted, if
adjustments were made.
(7) The MRV plan must be revised
and resubmitted to EPA by March 31 of
the calendar year following any of the
following events.
(i) The reporter is out of compliance
with its Underground Injection Control
permit (or relevant permit in the case of
a facility that is not under the
jurisdiction of the Safe Drinking Water
Act).
(ii) An EPA audit conducted under
the verification procedures of this part
determines it to be necessary.
(8) An MRV plan may be resubmitted
in any reporting year on a reporter’s
own volition.
(9) Each MRV plan and annual report
addendum must be submitted
electronically in a format specified by
the Administrator.
(b) [Reserved]
§ 98.449
Definitions.
All terms used in this subpart have
the same meaning given in the Clean Air
Act and subpart A of this part.
Leakage means the movement of CO2
from the injection zone to the surface,
including to the atmosphere, indoor air,
oceans or surface water.
Research and development means, for
the purposes of geologic sequestration
facility requirements in this subpart,
those projects receiving Federal funding
to research practices and monitoring
techniques that will enable safe and
effective long-term containment of a
gaseous, liquid, or supercritical CO2
stream in subsurface geologic
formations that are neither
demonstration nor commercial projects.
Separator means a vessel in which
streams of multiple phases are gravity
separated into individual streams of
single phase.
[FR Doc. 2010–6766 Filed 4–9–10; 8:45 am]
BILLING CODE 6560–50–P
E:\FR\FM\12APP2.SGM
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Agencies
[Federal Register Volume 75, Number 69 (Monday, April 12, 2010)]
[Proposed Rules]
[Pages 18576-18606]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2010-6766]
[[Page 18575]]
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Part II
Environmental Protection Agency
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40 CFR Part 98
Mandatory Reporting of Greenhouse Gases: Injection and Geologic
Sequestration of Carbon Dioxide; Proposed Rule
Federal Register / Vol. 75 , No. 69 / Monday, April 12, 2010 /
Proposed Rules
[[Page 18576]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 98
[EPA-HQ-OAR-2009-0926; FRL-9131-2]
RIN 2060-AP88
Mandatory Reporting of Greenhouse Gases: Injection and Geologic
Sequestration of Carbon Dioxide
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: EPA is proposing a rule to require reporting on carbon dioxide
(CO2) injection and geologic sequestration (GS). The
proposed rulemaking does not require control of greenhouse gases
(GHGs), rather it requires only monitoring and reporting of
CO2 injection and geologic sequestration. EPA first proposed
that suppliers of CO2 be subject to mandatory GHG reporting
requirements in April 2009 and finalized the rule for suppliers of
CO2 on October 30, 2009.
DATES: Comments. Comments must be received on or before June 11, 2010.
Public hearings. There will be one public hearing. The hearing date
and location is: April 19, 2010 from 9 a.m. to 1 p.m. at One Potomac
Yard, 2777 S. Crystal Drive, Arlington, VA 22202.
To obtain information about the public hearing or to register to
speak at the hearing, please go to https://www.epa.gov/climatechange/emissions/ghgrulemaking.html.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
OAR-2009-0926, by one of the following methods:
Federal eRulemaking Portal: https://www.regulations.gov. Follow the
online instructions for submitting comments.
E-mail: GHGReportingRR@epa.gov.
Fax: (202) 566-1741.
Mail: EPA Docket Center, Attention Docket OAR-2009-0926, Mailcode
2822T, 1200 Pennsylvania Ave., NW., Washington, DC 20460.
Hand/Courier Delivery: EPA Docket Center Public Reading Room, Room
3334, EPA West Building, Attention Docket OAR-2009-0926, 1301
Constitution Ave., NW., Washington, DC 20004. Such deliveries are only
accepted during the Docket's normal hours of operation, and special
arrangements should be made for deliveries of boxed information.
Instructions: Direct your comments to Docket ID No. EPA-HQ-OAR-
2009-0926. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
https://www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
confidential business information (CBI) or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI or otherwise protected through https://www.regulations.gov or e-mail. The https://www.regulations.gov Web site
is an ``anonymous access'' system, which means EPA will not know your
identity or contact information unless you provide it in the body of
your comment. If you send an e-mail comment directly to EPA without
going through https://www.regulations.gov your e-mail address will be
automatically captured and included as part of the comment that is
placed in the public docket and made available on the Internet. If you
submit an electronic comment, EPA recommends that you include your name
and other contact information in the body of your comment and with any
disk or CD-ROM you submit. If EPA cannot read your comment due to
technical difficulties and cannot contact you for clarification, EPA
may not be able to consider your comment. Electronic files should avoid
the use of special characters, any form of encryption, and be free of
any defects or viruses.
Docket: All documents in the docket are listed in the https://www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, will be publicly available only in hard copy.
Publicly available docket materials are available either electronically
in https://www.regulations.gov or in hard copy at EPA's Docket Center,
Public Reading Room, EPA West Building, Room 3334, 1301 Constitution
Ave., NW., Washington, DC. This Docket Facility is open from 8:30 a.m.
to 4:30 p.m., Monday through Friday, excluding legal holidays. The
telephone number for the Public Reading Room is (202) 566-1744, and the
telephone number for the Air Docket is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: For technical information, e-mail the
Greenhouse Gas Reporting Rule Hotline at ghgmrr@epa.gov with the name
of this action in the e-mail subject line, or contact Barbora Master,
Climate Change Division, Office of Atmospheric Programs (MC-6207J),
Environmental Protection Agency, 1200 Pennsylvania Ave., NW.,
Washington, DC 20460; telephone number: (202) 343-9899; fax number:
(202) 343-2359. To obtain information about the public hearings or to
register to speak at the hearings, please go to https://www.epa.gov/climatechange/emissions/ghgrulemaking.html.
SUPPLEMENTARY INFORMATION: Additional Information on Submitting
Comments: To expedite review of your comments by Agency staff, you are
encouraged to send a separate copy of your comments, in addition to the
copy you submit to the official docket, to Carole Cook, Climate Change
Division, Office of Atmospheric Programs (MC-6207J), Environmental
Protection Agency, 1200 Pennsylvania Ave., NW., Washington, DC 20460;
e-mail address: GHGReportingRule@epa.gov.
In drafting this proposed rulemaking, EPA reviewed and considered
comments submitted on the proposed subpart PP. However, as this is a
new proposal, EPA will not be responding to comments received on the
April 2009 proposed subpart PP in this rulemaking. To ensure that their
comments are considered, stakeholders should submit comments relevant
to this rulemaking as instructed in this document.
Regulated Entities. The Administrator has determined that this
action is subject to the provisions of Clean Air Act (CAA) section
307(d). See CAA section 307(d)(1)(V) (the provisions of CAA section
307(d) apply to ``such other actions as the Administrator may
determine''). This is a proposed regulation. If finalized, these
regulations would affect owners or operators of CO2
injection wells. Regulated categories and entities include those listed
in Table 1 of this preamble:
[[Page 18577]]
Table 1--Examples of Affected Entities by Category
------------------------------------------------------------------------
Examples of affected
Category NAICS facilities
------------------------------------------------------------------------
CO2 Enhanced Oil and Gas 211 Oil and gas extraction
Recovery Projects. projects using CO2
enhanced oil and gas
recovery.
GS Sites....................... N/A CO2 geologic
sequestration
projects.
------------------------------------------------------------------------
Table 1 of this preamble is not intended to be exhaustive, but
rather provides a guide for readers regarding facilities likely to be
affected by this action. Table 1 of this preamble lists the types of
facilities that EPA is now aware could be potentially affected by the
reporting requirements. Other types of facilities not listed in the
table could also be subject to reporting requirements. To determine
whether you are affected by this action, you should carefully examine
the applicability criteria found in proposed 40 CFR part 98, subpart A
or the relevant criteria in the sections related to the injection and
GS of CO2. If you have questions regarding the applicability
of this action to a particular facility, consult the person listed in
the preceding FOR FURTHER INFORMATION CONTACT section.
Some facilities that are affected by today's proposed rule have GHG
emissions from multiple source categories. Table 2 of this preamble has
been developed as a guide to help potential CO2 injection
and GS reporters subject to the proposed rule identify the source
categories (by subpart) that they may need to (1) consider in their
facility applicability determination, and/or (2) include in their
reporting. The table should only be seen as a guide. Additional
subparts in 40 CFR part 98 may be relevant for a given reporter.
Similarly, not all listed subparts are relevant for all reporters.
Table 2--Source Categories and Relevant Subparts
------------------------------------------------------------------------
Other subparts recommended for
Source category (and main applicable review to determine
subpart) applicability
------------------------------------------------------------------------
Injection and Geologic Sequestration of 40 CFR part 98, subpart C.
Carbon Dioxide.
40 CFR part 98, subpart W
(proposed).
40 CFR part 98, subpart PP.
------------------------------------------------------------------------
Acronyms and Abbreviations. The following acronyms and
abbreviations are used in this document.
3-D three-dimensional
CAA Clean Air Act
CBI confidential business information
CCS carbon dioxide capture and geologic sequestration
CDM Clean Development Mechanism
CFR Code of Federal Regulations
CH4 methane
CO2 carbon dioxide
DOE Department of Energy
EC European Commission
ECBM enhanced coalbed methane
EIA Economic Impact Analysis
EPA Environmental Protection Agency
EO Executive Order
ER enhanced oil and gas recovery
GHG greenhouse gas
GPG Good Practice Guidance
GS geologic sequestration
HFC hydrofluorocarbon
HFE hydrofluoroether
ICR Information Collection Request
IMO International Maritime Organization
IPCC Intergovernmental Panel on Climate Change
IRS Internal Revenue Service
MRR Mandatory Reporting of Greenhouse Gases Rule
MRV monitoring, reporting, and verification
N2O nitrous oxide
NAICS North American Industry Classification System
NTTAA National Technology Transfer and Advancement Act
O&GJ Oil and Gas Journal
OAR Office of Air and Radiation
OMB Office of Management and Budget
OW Office of Water
PFC perfluorocarbon
QA/QC quality assurance/quality control
R&D research and development
RFA Regulatory Flexibility Act
SBREFA Small Business Regulatory Enforcement Fairness Act
SDWA Safe Drinking Water Act
SF6 sulfur hexafluoride
TSD technical support document
UIC Underground Injection Control
UNFCCC United Nations Framework Convention on Climate Change
US United States
UMRA Unfunded Mandates Reform Act of 1995
USDA United States Department of Agriculture
USDW underground source of drinking water
VEF Vulnerability Evaluation Framework
Table of Contents
I. Background
A. Organization of This Preamble
B. Background on the Proposed Rule
C. Overview of the Proposal
D. Legal Authority
E. Relationship to the Proposed UIC Class VI Rulemaking Under
the Safe Drinking Water Act
F. Relationship to Other CO2 Injection Information
Collection and Reporting Efforts
II. Rationale for Reporting, Recordkeeping and Verification
Requirements
A. Definition of Reporting Facilities
B. Selection of Reporting Thresholds
C. Selection of Data To Be Reported
D. Selection of Monitoring, Reporting, and Verification (MRV)
Plan Requirements and Approval Process
E. Selection of Schedule and Process for Reporting
F. Selection of Procedures for Estimating Missing Data
G. Selection of Records to Retain
III. Economic Impacts of the Proposed Rule
A. How were compliance costs estimated?
B. What are the costs of the proposed rule?
C. What are the economic impacts of the proposed rule?
D. What are the impacts of the proposed rule on small
businesses?
E. What are the benefits of the proposed rule for society?
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act (RFA)
D. Unfunded Mandates Reform Act (UMRA)
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health Risks and Safety Risks
H. Executive Order 13211: Actions That Significantly Affect
Energy Supply, Distribution, or Use
I. National Technology Transfer and Advancement Act
J. Executive Order 12898: Federal Actions to Address
Environmental Justice in Minority Populations and Low-Income
Populations
[[Page 18578]]
I. Background
A. Organization of This Preamble
This preamble is broken into several large sections, as detailed in
the Table of Contents. The following paragraphs describe the layout of
the preamble and provide a brief summary of each section.
Section I of this preamble contains the basic background
information about the origin of this proposed rulemaking, including a
discussion of how it relates to the finalized requirements for
Suppliers of CO2 (under 40 CFR, part 98, subpart PP) and to
the Underground Injection Control (UIC) program. This section also
discusses EPA's legal authority under the Clean Air Act (CAA) to
collect the proposed data, and the benefits of collecting the data.
Section II of this preamble summarizes the general provisions of
this proposed rulemaking for reporting CO2 injection and GS.
This section also provides a brief summary of, and rationale for, the
selection of key design elements. Specifically, this section describes
EPA's rationale for the proposed (i) definition of reporting
facilities, (ii) applicability thresholds, (iii) data reporting
requirements, (iv) monitoring, reporting and verification (MRV) plan
requirements and process, (v) schedule and process for reporting, (vi)
procedures for estimating missing data, and (vii) recordkeeping
requirements. Thus, for example, there is a specific discussion
regarding appropriate applicability thresholds, monitoring
methodologies and reporting and recordkeeping requirements for all
CO2 injection facilities, and additional requirements for
facilities that conduct GS. EPA describes the proposed options for each
design element as well as the other options considered. Throughout this
discussion, EPA highlights specific issues on which the Agency solicits
comment.
Section III of this preamble provides the summary of the cost
impacts, economic impacts, and benefits of this proposed rule from the
Economic Impact Analysis (EIA). Finally, Section IV of this preamble
discusses the various statutory and executive order requirements
applicable to this proposed rulemaking.
B. Background on the Proposed Rule
On December 26, 2007, President Bush signed the fiscal year 2008
Consolidated Appropriations Act authorizing funding for EPA to issue a
rule requiring the mandatory reporting of greenhouse gas (GHG)
emissions (Consolidated Appropriations Act, 2008, Pub. L. 110-161, 121
Stat. 1844, 2128 (2008)). An accompanying joint explanatory statement
directed EPA to ``use its existing authority under the Clean Air Act''
to develop a mandatory GHG reporting rule.
The proposed Mandatory Reporting of Greenhouse Gases Rule (MRR) was
signed on March 10, 2009, by Administrator Lisa Jackson and was
published a month later (74 FR 16448, April 10, 2009). After a 60-day
comment period, two public hearings, and meeting with over 4,000
additional people in over 150 groups via Webinars, conferences,
individual meetings, and other forms of outreach, EPA issued a final
rule on October 30, 2009 (74 FR 56260). The MRR requires reporting of
GHG emissions and supply from all sectors of the economy, including
fossil fuel suppliers, industrial gas suppliers, and direct emitters of
GHGs. The rule does not require the control of GHGs; rather the rule
requires only that sources above certain threshold levels monitor and
report those GHGs.
The final MRR covers the major GHGs that are directly emitted by
anthropogenic activities. These include carbon dioxide
(CO2), methane (CH4), nitrous oxide
(N2O), hydrofluorocarbons (HFCs), perfluorocarbons (PFCs),
sulfur hexafluoride (SF6), and other specified fluorinated
compounds (e.g., hydrofluoroethers (HFEs)) used in boutique
applications such as electronics and anesthetics.\1\
---------------------------------------------------------------------------
\1\ These gases influence the climate system by trapping in the
atmosphere heat that would otherwise escape to space. Additional
information about GHGs, climate change, climate science, and other
related issues, can be found at EPA's climate change Web site at
https://www.epa.gov/climatechange/.
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The final rule contains 31 subparts, each requiring reporting from
a defined source category. In order to meet the reporting time, quality
assurance, and verification requirements of the rule, EPA is
establishing a facility-to-EPA electronic reporting system to
facilitate collection of data under this rule. All facilities that are
covered under this rule as reporters will use this data system to
submit required data.
Subpart PP requires the reporting of CO2 supplied to the
economy. Subpart PP applies to all facilities with CO2
production wells, facilities with production process units that capture
and supply CO2 for commercial applications or that capture
and maintain custody of a CO2 stream to sequester or
otherwise inject it underground, and to importers and exporters of bulk
CO2. During the public comment period on the rule, EPA
received many comments on subpart PP that CO2 injected
underground should be considered when estimating emissions from the
CO2 supply industry. Some commenters specified that some of
the CO2 supplied for the purposes of enhanced oil and gas
recovery (ER) is additionally sequestered rather than emitted and
characterized ER operations as ``closed systems'' rather than emissive.
Other commenters stated that including reporting requirements for
geologically sequestered CO2 would fill a critical gap in
the reporting system. EPA agrees that ER is a potentially non-emissive
end use and that GS data reporting from ER sites can assist EPA in
quantifying the amount of CO2 that is permanently and
securely geologically sequestered. In addition, EPA agrees that GS
reporting requirements would provide information and transparency on
the amount of CO2 injected and geologically sequestered in
the United States.
Although CCS is occurring now on a relatively small scale, it could
play a larger role in mitigating GHG emissions from a wide variety of
stationary sources. According to the Inventory of U.S. Greenhouse Gas
Emissions and Sinks: 1990-2007, stationary sources contributed 67
percent of the total CO2 emissions from fossil fuel
combustion in 2007.\2\ These sources represent a wide variety of
sectors amenable to CO2 capture: electric power plants
(existing and new), natural gas processing facilities, petroleum
refineries, iron & steel foundries, ethylene plants, hydrogen
production facilities, ammonia refineries, ethanol production
facilities, ethylene oxide plants, and cement kilns. Furthermore, 95
percent of the 500 largest stationary sources are within 50 miles of a
candidate GS reservoir.\3\ Estimated GS capacity in the United States
is over 3,500 Gigatons CO2 (GtCO2) (13,000
Gigatons CO2 at the high end),\4\ although the actual
capacity may be lower once site-specific technical and economic
considerations are addressed. Even if only a fraction of that geologic
capacity is used, CCS is poised to play a sizeable role in mitigating
U.S. GHG emissions.
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\2\ U.S. EPA Draft Inventory of U.S. Greenhouse Gas Emissions
and Sinks, 1990-2007, Draft Report, EPA 430-R-09-004. Available at:
https://epa.gov/climatechange/emissions/usinventoryreport.html.
\3\ Dooley, JJ, CL Davidson, RT Dahowski, MA Wise, N Gupta, SH
Kim, EL Malone. 2006. ``Carbon Dioxide Capture and Geologic Storage:
A Key Component of a Global Energy Technology Strategy to Address
Climate Change.'' Joint Global Change Research Institute, Battelle
Pacific Northwest Division. PNWD-3602.
\4\ DOE. 2008. Carbon Sequestration Atlas of the United States
and Canada (Atlas II). Available at: https://www.netl.doe.gov/technologies/carbon_seq/refshelf/atlasII/.
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Many of the injection and monitoring technologies that may be
applicable for
[[Page 18579]]
GS are commercially available today and will be more widely
demonstrated over the next 10 to 15 years.\5\ The oil and natural gas
industry in the United States has over 35 years of experience of
injection and monitoring of CO2 in the deep subsurface for
the purposes of enhancing oil and natural gas production. This
experience provides a strong foundation for the injection and
monitoring technologies that will be needed for commercial-scale CCS.
U.S. experience with ER combined with the experience of four end-to-end
commercial CCS projects \6\ and ongoing research, demonstration, and
deployment programs throughout the world, are building confidence that
geologic sequestration of large amounts of CO2 can be
achieved.
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\5\ Dooley, JJ, CL Davidson, RT Dahowski. 2009. ``An Assessment
of the Commercial Availability of Carbon Dioxide Capture and Storage
Technologies as of June 2009.'' Joint Global Change Research
Institute. Pacific Northwest National Laboratory. PNNL-18520.
\6\ These projects are: Sleipner (Norwegian North Sea)--1 Mt
CO2/yr injected since 1996; Weyburn (Canada)--1 Mt
CO2/yr injected since 2000; In Salah (Algeria)--1.2 Mt
CO2/yr injected since 2004; and Snohvite (Norwegian
Barents Sea)--0.7 Mt CO2/yr injected since 2008.
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C. Overview of the Proposal
Today, EPA is proposing to amend the Mandatory Reporting of
Greenhouse Gases Program at 40 CFR part 98 to add reporting
requirements covering facilities that conduct injection and geologic
sequestration of CO2.
EPA is proposing a tiered approach for reporting requirements under
this subpart. The first tier of proposed regulations would establish a
set of reporting requirements that would cover all facilities that
inject CO2 underground. As described in Section II.C of this
preamble, all facilities would be required to report CO2
transferred onsite from offsite sources, the source of the
CO2 (if known), and CO2 injected underground.
The second tier of reporting requirements would apply to GS
facilities. As described in Section II.C of this preamble, GS
facilities would be required to calculate CO2 sequestered by
subtracting total CO2 emissions from the CO2
injected in the reporting year. The emitted quantity would include the
injected CO2 that leaked from the subsurface to the surface
(if any), CO2 produced with oil or natural gas where ER
operations are conducted at the GS facility, fugitive or vented
CO2 emissions from surface equipment, and emissions from
combustion sources located within the facility boundary, such as
compressors.
EPA considered several options for monitoring, reporting and
verification (MRV) of potential CO2 leakage \7\ at GS sites:
do not require a MRV plan, require a universal MRV plan that applies to
all GS sites, or require a site-specific MRV plan. EPA is proposing to
require monitoring according to a site-specific MRV plan, but is
seeking comment on all of the options considered. While the risk of
leakage at a well-selected and well-managed GS site is expected to be
low, the Agency considers it important for all facilities conducting GS
to demonstrate that they have met MRV standards. The options described
above are discussed in more detail in Section II.D of this preamble.
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\7\ Leakage in this proposed rule is defined as the movement of
CO2 from the injection zone to the surface (for example
to the atmosphere, indoor air, oceans or surface water).
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Data on CO2 injection and GS are critical to informing
CAA GHG policies. This data would provide information and transparency
on the amount of CO2 injected and geologically sequestered
in the United States and, in combination with other subparts of the
MRR, would enable EPA to track the flow of CO2 across a CCS
system. In addition, this information would enable EPA to monitor the
growth and efficacy of GS (and therefore CCS) as a GHG mitigation
technology over time and to evaluate relevant policy options. For
example, EPA would be able to track whether incentives or regulations
are needed to encourage faster or further GS project development. EPA
would also be able to track whether ER sites are reporting GS and
consider whether incentives or regulations are needed. Where ER
facilities are reporting GS, EPA would be able to evaluate ER as a
potentially non-emissive end use. In combination with subpart PP, EPA
would be able to reconcile this data with CO2 supplied in
order to better understand the quantity of CO2 supplied to
emissive and non-emissive end uses. Furthermore, this data would inform
Agency policy decisions under CAA sections 111 and 112 related to the
use of CCS for mitigating GHG emissions.
In developing this proposal, EPA considered overlap between this
program and other programs. In July 2008, EPA proposed to amend its UIC
program to establish a new class of injection well for GS projects (73
FR 43492 (July 25, 2008)). Today's proposal provides a pathway for
CO2 injection facilities to report to EPA as GS facilities
under the CAA, regardless of their UIC permit classification. Under
this proposal, any facility sequestering CO2 underground can
choose to qualify and report as a GS facility for purposes of this
proposed rule.
Since subpart RR is an amendment to the MRR, the general provisions
of the MRR (40 CFR part 98, subpart A) apply to today's proposed
subpart RR unless a provision is superseded by this subpart that
applies uniquely to facilities that inject CO2 or that
conduct GS. The general provisions address the following topics: The
purpose and scope (40 CFR 98.1); who must report (40 CFR 98.2); the
general monitoring, reporting, recordkeeping and verification
requirement (40 CFR 98.3); the authorization and responsibilities of
the designated authority (40 CFR 98.4); how a report is submitted (40
CFR 98.5); definitions (40 CFR 98.6); the standardized methods
incorporated by reference (40 CFR 98.7); the compliance and enforcement
provisions (40 CFR 98.8); and the mailing addresses (40 CFR 98.9).
Amendments to the General Provisions. In a separate rulemaking,
package that was recently published (March 16, 2010), EPA issued minor
harmonizing changes to the general provisions for the GHG reporting
rule (40 CFR part 98, subpart A) to accommodate the addition of source
categories not included in the 2009 final rule (e.g., subparts proposed
in April 2009 but not finalized in 2009, any new subparts that may be
proposed in the future). The changes update 98.2(a) on rule
applicability and 98.3 regarding the reporting schedule to accommodate
any additional subparts and the schedule for their reporting
obligations (e.g., source categories finalized in 2010 would not begin
data collection until 2011 and reporting in 2012).
In particular, we restructured 40 CFR 98.2(a) to move the lists of
source categories from the text into tables. A table format improves
clarity and facilitates the addition of source categories that were not
included in calendar year 2010 reporting and would begin reporting in
future years. A table, versus list, approach allows other sections of
the rule to be updated automatically when the table is updated; a list
approach requires separate updates to the various list references each
time the list is changed. In addition to reformatting the 98.2(a)(1)-
(2) lists into tables, other sections of subpart A were reworded to
refer to the source category tables because the tables make it clear
which source categories are to be considered for determining the
applicability threshold and reporting requirements for calendar years
2010, 2011, and future years.
[[Page 18580]]
As part of today's proposed rule, EPA is proposing changes to
subpart A to accommodate subpart RR. Because all CO2
injection and geologic sequestration facilities (as defined in proposed
40 CFR part 98, subpart RR) would be subject to proposed subpart RR,
EPA is proposing that this source category be added to the table of
``all-in'' source categories referenced from 40 CFR 98.2(a)(1).\8\ For
facilities that become subject to the MRR due to CO2
injection or geologic sequestration, the first annual GHG report would
cover calendar year 2011 rather than 2010.
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\8\ Since we changed the list of covered subcategories to
tables, we are not providing regulatory text in this proposal
because the preamble is clear.
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EPA is proposing to amend 40 CFR 98.2(a) so that the MRR applies to
facilities located on or under the Outer Continental Shelf. These
revisions are necessary to ensure that any CO2 injection or
GS facilities located on or under the Outer Continental Shelf of the
United States would be required to report. In addition, EPA is
proposing revisions to the definition of United States to clarify that
the United States includes the territorial seas. Other facilities
located offshore of the United States covered by the MRR program at 40
CFR part 98 would also be affected by this change in the definition of
United States. For example, EPA is proposing in a separate rule to
revise the MRR requirements to add a new subpart, subpart W, to address
petroleum and natural gas systems. Any comments specific to that issue
should be directed to the Agency in that rulemaking, not this one.
Finally, in addition to the change to the definition of United States,
EPA is adding a definition of ``Outer Continental Shelf.'' This
definition is drawn from the definition in the U.S. Code. Together,
these changes make clear that the MRR applies to facilities on land, in
the territorial seas, or on or under the Outer Continental Shelf of the
United States, and that otherwise meet the applicability criteria of
the MRR.
EPA also is proposing to amend 40 CFR 98.7 (incorporation by
reference) to include standard methods used in proposed subpart RR.
D. Legal Authority
EPA is proposing subpart RR under the existing authority provided
in CAA section 114. As noted in the MRR, CAA section 114 provides EPA
with broad authority to require information mandated by this rule
because such data will inform and are relevant to EPA's carrying out a
wide variety of CAA provisions (74 FR 66264). Under CAA section
114(a)(1), the Administrator may require emissions sources, persons
subject to the CAA, or persons whom the Administrator believes may have
necessary information to monitor and report emissions and provide such
other information as the Administrator requests for the purposes of
carrying out the provisions in the CAA (except for a provision of title
II with respect to motor vehicles).
As discussed in greater detail in the response to comments for the
final MRR, the CAA provides EPA with broad authority to require the
comprehensive and accurate information mandated in this rule because
such data will inform, and are relevant to, EPA's analyses of various
CAA provisions (Mandatory Reporting of Greenhouse Gases, EPA's Response
to Public Comment's Section 3-Legal Issues). EPA may gather information
for a variety of purposes, including for the purpose of assisting in
the development of implementation plans or of emissions standards under
CAA section 111, determining compliance with implementation plans or
such standards, or more broadly for ``carrying out any provision'' of
the CAA. In addition, CAA section 103 authorizes EPA to establish a
national research and development program, including non-regulatory
approaches and technologies for the prevention and control of air
pollution as it relates to GHGs and climate change.
The information from CO2 injection and GS facilities
will allow EPA to make well-informed decisions about whether and how to
use the CAA to regulate these facilities and encourage voluntary
reductions.
E. Relationship to the Proposed UIC Class VI Rulemaking Under the Safe
Water Drinking Act
The Agency maintains a high-level of coordination across EPA
offices and regions on GS activities and regulatory development. EPA's
Office of Air and Radiation (OAR) and Office of Water (OW) work closely
to promote safe and effective implementation of GS technologies while
ensuring protection of human health and the environment. All Agency
efforts related to GS, including the UIC Class VI proposal which is
discussed in more detail below, and this MRR proposal, are closely
coordinated.
EPA's UIC program was established in the 1970s to prevent
endangerment of underground sources of drinking water (USDWs) from
injection of various fluids, including CO2 for ER, oil field
fluids, water stored for drinking water supplies, and municipal and
industrial waste. The UIC program, which is authorized by Part C of the
Safe Drinking Water Act (SDWA) (42 U.S.C. 300h et seq.), is designed to
prevent the movement of such fluid into USDWs by addressing the
potential pathways through which injected fluids can migrate and
potentially endanger USDWs.
When EPA initially promulgated its UIC program regulations, the
Agency defined five classes of injection wells at 40 CFR 144.6, based
on similarities in the fluids injected, construction, injection depth,
design, and operating techniques. Wells injecting industrial non-
hazardous liquids, municipal wastewaters or hazardous wastes beneath
the lowermost USDW are categorized as Class I. Those injecting fluids
in connection with conventional oil or natural gas production, enhanced
oil and gas production, and the storage of hydrocarbons which are
liquid at standard temperature and pressure are categorized as Class
II. Class III wells inject fluids associated with the extraction of
minerals, and those categorized as Class IV inject hazardous or
radioactive wastes into or above USDWs. Class IV injection wells are
banned unless authorized under an approved Federal or State ground
water remediation project. Class V includes all injection wells that
are not included in Classes I-IV. This well class provides for Class V
experimental technology wells including those permitted as GS pilot
projects.\9\
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\9\ See EPA UIC Guidance 83. Available at: https://www.epa.gov/safewater/uic/wells_sequestration.html.
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In 2008, EPA proposed to amend the UIC program to establish a new
class of injection well--Class VI--to cover the underground injection
of CO2 for the purpose of GS, or long-term storage of
CO2 (73 FR 43492, July 25, 2008). The proposed requirements
would tailor existing components of the UIC program to address the
unique nature of GS projects so as to ensure that the injection of
large volumes of CO2 in a variety of geologic formations for
the purposes of long term storage would not endanger USDWs. The UIC
Class VI proposal does not require any facilities to capture and/or
sequester CO2; rather the proposed requirements, if
finalized, would protect USDWs under the SDWA. The SDWA does not
provide authority to develop regulations for all areas related to GS
such as capture or transport. As outlined in the UIC Class VI proposal,
injection wells used for injecting CO2 for the purposes of
ER would continue to be regulated and permitted as Class II as long as
any
[[Page 18581]]
production is occurring. EPA received significant comments on this
proposed approach and is currently evaluating these comments for the
final rulemaking.
Facilities regulated under the UIC program are required to collect
and report data, with minimum requirements for the collection and
reporting of data established at the Federal level. Where States are
given primacy over the UIC program, the data collected under the UIC
program varies. Data currently collected under a State-issued UIC
permit is submitted to States while, under today's subpart RR proposal,
reporters will be submitting data directly to EPA. The Agency believes
that State, local, and tribal input is valuable in ensuring that the
subpart RR reporting requirements appropriately build on the UIC
program requirements. EPA is seeking comment on a number of topics and
will look for opportunities to conduct outreach with State, local and
tribal organizations between proposal and finalization.
Today's proposal builds on the UIC program requirements for
monitoring with the additional goals of verifying the amount of
CO2 sequestered and collecting data on CO2
surface emissions from GS facilities. As described in Section II.D of
this preamble, EPA is proposing that a facility's UIC permit may be
used to demonstrate that certain MRV plan requirements have been
fulfilled.
In the Agency's August 2009 Notice of Data Availability
supplementing the UIC Class VI proposal, EPA noted that it was
evaluating the need for a more comprehensive regulatory framework for
GS. The Agency acknowledges that regulatory clarity is essential for
enabling GS to move forward in a manner that protects human health and
the environment. It is EPA's intention to coordinate GS requirements
across relevant statutory or other programs in order to minimize any
redundancies and increase clarity for stakeholders. The Agency seeks
comment on whether this is appropriate.
The proposed UIC Class VI rule is a separate rulemaking action; the
comment period for that rulemaking closed on December 24, 2008. EPA
will not be accepting or responding to comments on the proposed UIC
Class VI rule through today's proposal unless related to a specific
issue raised by this action.
F. Relationship to Other CO2 Injection Information
Collection and Reporting Efforts
In considering how to design this proposal, EPA reviewed and took
into account other domestic and international reporting and monitoring
programs. Key programs are summarized in this section.
The Department of Energy (DOE) Energy Information Administration
implements a voluntary GHG reporting program under section 1605(b) of
the Energy Policy Act of 1992, which directed DOE to issue guidelines
establishing a voluntary greenhouse gas reporting program (42 U.S.C.
13385(b)). Under the Energy Information Administration's ``1605(b)
program,'' reporters can choose to prepare an entity-wide GHG inventory
and identify specific GHG reductions made by the entity.\10\ Reporting
tools were revised and published in 2009 to assist entities in
preparing a preliminary estimate of emissions. The 2007 updated 1605(b)
guidance outlines a voluntary process to report data on CO2
sequestration. Currently, no CO2 injection or sequestration
entity has reported under the 1605(b) program per the 2007 guidelines.
According to the Energy Information Administration Web site, the first
reporting cycle under the revised Voluntary Reporting of Greenhouse
Gases Program has not been completed as of January 15, 2010. The Energy
Information Administration anticipates issuing an annual report and
public use database for data reported through 2008 by early 2010.\11\
The 1605(b) guidance requires the implementation of a site-specific
monitoring plan, but this plan is not evaluated by DOE to determine
whether the plan will provide for appropriate monitoring. Four
prescriptive monitoring scenarios are offered with grades ranging from
``A'' to ``C'', any of which would be acceptable for compliance with
the 1605(b) program. Furthermore, although the 1605(b) guidance cites
the importance of reporting CO2 leakage should it occur, the
guidance does not include a discussion of, procedures for, or
methodologies for using monitoring technologies and techniques to
quantify the leakage. As a result of this, and the fact that reporting
is voluntary, the 1605(b) program would not meet the data needs of this
proposed rule.
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\10\ Under the 1605(b) program an ``entity'' is defined as ``the
whole or part of any business, institution, organization or
household that is recognized as an entity under any U.S. Federal,
State or local law that applies to it; is located, at least in part,
in the U.S.; and whose operations affect U.S. greenhouse gas
emissions.'' Available at: https://www.pi.energy.gov/enhancingGHGregistry.
\11\ Available at: https://www.eia.doe.gov/oiaf/1605/data_reports.html.
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The Internal Revenue Service (IRS) made public IRS Notice 2009-83
Credit for Carbon Dioxide Sequestration under section 45Q on its Web
site on October 8, 2009.\12\ The notice provides procedures for the
allocation of credits for CO2 sequestration under section
45Q of the Internal Revenue Code. Section 45Q was enacted by section
115 of the Energy Improvement and Extension Act of 2008, (October 3,
2008) and was amended by section 1131 of the American Recovery and
Reinvestment Act of 2009 (February 17, 2009). To claim this credit, a
taxpayer must follow general monitoring and verification principles,
calculate CO2 sequestered in the fiscal year using a mass-
balance equation, and report to IRS the amount of qualified
CO2 sequestered in the fiscal year. Seventy-five million
metric tons of qualified CO2 can be taken into account for
this credit. The IRS included a provision in the notice to supersede
its monitoring and verification procedures and requirements with
procedures and requirements finalized by EPA in future GS rulemaking
such as the UIC Class VI proposal and this proposed rule.
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\12\ Available at: https://www.irs.gov/irb/2009-44_IRB/ar11.html.
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EPA has concluded for a number of reasons that the IRS data would
not meet the needs outlined in this proposed rule. First, the IRS
reporting requirement will expire after 75 million metric tons of
CO2 is reported as sequestered to IRS, at which point the
data collection will end. Second, the level of reporting and
transparency would not meet the verification needs of this proposed
rule. GS facilities only report the quantity of CO2
sequestered to IRS. The data used to calculate sequestration and the
specific monitoring procedures followed will only be reviewed by IRS
staff in the case of an audit. Given the variability in geology and
other conditions at GS facilities, EPA believes that the monitoring
approach at each GS facility must be reviewed on a case-by-case basis
to ensure that it is appropriate for the site-specific geologic and
operational conditions. Third, the IRS does not outline procedures or
provide a mechanism for quantifying and reporting any CO2
leakage that may occur as is necessary for this proposed rule.
EPA notes that the United States submits an inventory of GHG
emissions that accounts for CCS to the Secretariat of the United
Nations Framework Convention on Climate Change (UNFCCC) each year. The
UNFCCC, ratified by the United States in 1992, establishes an overall
framework for intergovernmental efforts to tackle the
[[Page 18582]]
challenge posed by climate change. The United States has submitted the
Inventory of U.S. Greenhouse Gas Emissions and Sinks (Inventory) to the
United Nations every year since 1993. The annual Inventory is
consistent with national inventory data submitted by other UNFCCC
parties, and uses internationally accepted methods for its emission
estimates. For more information about the Inventory, please refer to
the following Web site: https://www.epa.gov/climatechange/emissions/usinventoryreport.htm.
The United States currently follows the 1996 \13\ Intergovernmental
Panel of Climate Change (IPCC) guidelines in preparing its Inventory,
as supplemented by IPCC Good Practice Guidance (GPG) from 2000 \14\ and
2003 \15\. Since these guidelines do not provide information on the
accounting of GS, EPA addressed CO2 usage in the 2007
Inventory by accepting some general, top-down assumptions about the
end-use of supplied CO2. First, EPA collected CO2
production data for natural CO2 domes and estimated for each
dome the amount of CO2 used for ER operations and the amount
of CO2 used for non-ER operations. EPA assumed that the
percentage of naturally produced CO2 used for non-ER
operations (e.g., food processing, chemical production) was all emitted
to the atmosphere. The percentage used for ER operations was assumed to
be sequestered. Second, EPA collected data from industry on
anthropogenic CO2 emitted from natural gas processing and
ammonia plants and accounted it as emitted, regardless of whether the
CO2 was captured or not.
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\13\ IPCC, 1996. ``Revised 1996 IPCC Guidelines for National
Greenhouse Gas Inventories.'' National Greenhouse Gas Inventories
Programme. Available: https://www.ipcc-nggip.iges.or.jp/public/gl/invs1.html.
\14\ IPCC. 2000. ``Good Practice Guidance and Uncertainty
Management in National Greenhouse Gas Inventories.'' National
Greehouse Gas Inventories Programme. Available at: https://www.ipcc-nggip.iges.or.jp/public/gp/english/.
\15\ IPCC. 2003. ``Good Practice Guidance for Land Use, Land-Use
Change, and Forestry.'' National Greenhouse Gas Inventories
Programme. Available at: https://www.ipcc-nggip.iges.or.jp/public/gpglulucf/gpglulucf.html.
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The IPCC published new inventory guidelines in 2006 \16\, which
directly address accounting for GS and include methodologies for the
estimation of emissions from capture, transport, injection, and GS of
CO2. The guidelines are based on the principle that the CCS
system should be accounted for in a complete and consistent manner
across the entire Inventory. The approach accounts for CO2
produced from natural CO2 domes and captured at industrial
facilities as well as emissions from capture, transport, and use. For
GS specifically, the IPCC guidelines outline a Tier 3 methodology \17\
for estimating and reporting emissions based on site-specific
evaluations of each storage site. EPA believes that the GS monitoring,
reporting, and verification requirements of this proposed rule are
consistent with the 2006 IPCC guidelines.
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\16\ 2006 IPCC Guidelines for National Greenhouse Gas
Inventories: Volume 2--Energy. Chapter 5 Carbon Dioxide Transport,
Injection, and Geological Storage. Available at: https://www.ipcc-nggip.iges.or.jp/public/2006gl/index.htm.
\17\ Tier 3 methods include either detailed emission models or
measurements and data at individual plant level where appropriate.
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In considering how to design this proposal, EPA also took into
account the monitoring requirements adopted in other countries, in
particular other UNFCCC member countries that have already taken steps
towards collecting information for CCS to meet the 2006 IPCC
guidelines. The Directive of the European Parliament and of the Council
on the geological storage of carbon dioxide (Commission decision 2007/
589/EC) establishes a legal framework for the environmentally safe
geological storage of CO2. It requires European Council (EC)
member States to ensure that each GS site operator will carry out
monitoring of the injection facilities, the storage complex (including
the CO2 plume), and, where appropriate, the surrounding
environment for detection of any significant migration or leakage of
CO2 or any significant adverse effect on the surrounding
environment.
The directive requires that monitoring frequency be determined by
the competent authority, and should be at least once a year. A
monitoring report should be developed that describes the quantities and
properties of the CO2 streams delivered and injected,
including concentration of the CO2 streams, in the reporting
period. The parameters to be monitored include:
Fugitive emissions of CO2 at the injection
facility;
CO2 volumetric flow at injection wellheads;
CO2 pressure and temperature at injection
wellheads (to determine mass flow);
Chemical analysis of the injected material; and
Reservoir temperature and pressure (to determine
CO2 phase behavior and state).
Per the directive, each GS site should choose monitoring technology
based on best practices available at the time the monitoring plan is
designed. The following options should be considered and used when
appropriate:
Technologies that can detect the presence, location, and
migration paths of CO2 in the subsurface and at the surface;
Technologies that provide information about pressure-
volume behavior and aerial/vertical distribution of CO2-
plume to refine numerical 3-D-simulation to the 3-D-geological models
of the storage formation; and
Technologies that can provide a wide aerial spread in
order to capture information on any previously undetected potential
leakage pathways across the aerial dimensions of the complete storage
complex and beyond, in the event of significant irregularities or
migration of CO2 out of the storage complex.
In Australia, the Proposed Greenhouse Gas Geological Sequestration
Regulations 2009 were proposed to support the implementation and
administration of the Greenhouse Gas Geological Sequestration Act 2008
and to address several CCS related issues, including monitoring
requirements for GS. These regulations require that each GS site
develop a monitoring and verification plan which includes the
following:
Characteristics of the geological formation into which the
GHG substance is to be injected and any geological or other conditions
that may influence containment of a stored GHG;
A description of the existing environment above, on and
below the surface of the ground; and any resource above, on and below
the surface of the ground that a person is entitled to extract or use
under a resource authority;
Details of the equipment proposed to be used to monitor
the behavior of stored greenhouse gas substances, and where it is to be
located;
Details of the techniques to be used to monitor, the
length of time that each technique is to be used, and how often each
monitoring technique is to be carried out; and
The regulation also specifies that a report on the outcome
of all monitoring and verification activities carried out should be
completed quarterly.
Other international efforts have also been useful to EPA in
developing the requirements of this proposed rule. The International
Maritime Organization (IMO) has published under the London Protocol
\18\ two documents to provide guidelines to parties for the assessment
of and implementation of disposal of CO2 in sub-seabed
geologic formations:
[[Page 18583]]
Specific Guidelines for Assessment of Carbon Dioxide Streams for
Disposal into Sub-Seabed Geological Formations (2009) and Risk
Assessment and Management Framework for CO2 Sequestration in
Sub-Seabed Geological Structures (2007). These guidelines focus on
several aspects of CCS including:
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\18\ Available at: https://www.imo.org/includes/blastData.asp/doc_id=10531/9%20%20CO2%20Sequestration%20English.pdf.
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CO2 stream characterization (chemical and
physical properties);
Waste prevention audit;
Consideration of waste management options;
Action lists;
Identification and characterization of sub-seabed
geological formation;
Assessment of potential impacts;
Monitoring and risk management; and
Permitting and permit condition.
Under the Kyoto Protocol, the Clean Development Mechanism (CDM) is
a market-based mechanism that aids countries in meeting their emission
limitation and reduction goals through emission reduction (or removal)
projects in developing nations. These projects allow companies in
industrialized countries to receive credits that can either be put
towards their emission limitation or reduction, traded, or sold. Two
new proposed CDM methodologies (NM0167 and NM0168) address CCS
activities.\19\ These new baseline and monitoring methodologies have
not yet been approved by the CDM Executive Board, but EPA continues to
follow their progress and to monitor for other GS methodology
proposals.
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\19\ Available at: https://cdm.unfccc.int/about/ccs/.
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II. Rationale for Reporting, Recordkeeping, and Verification
Requirements
A. Definition of Reporting Facilities
1. CO2 Injection Facility
EPA is proposing that the CO2 injection facility be
defined broadly to cover wells or a group of wells that inject
CO2 into the subsurface or sub-seabed geologic formations.
This definition would encompass both onshore and offshore facilities.
EPA is proposing a broad definition of CO2 injection
facility to ensure complete reporting of basic information regarding
the CO2 transferred onsite, the source of the CO2
if known, and the CO2 injected. The broad definition also
provides reporters with flexibility either to report this basic
information on a well by well basis or to group wells in an area for
reporting purposes. Given the proposed threshold and applicability for
CO2 injection facilities, a more specific definition
addressing the aggregation of groups of wells in an area is not
necessary. As discussed in more detail in Section II.B of this
preamble, however, EPA is soliciting comment on the question of how to
define the source category if a more precise definition is necessary.
2. GS Facility
EPA is proposing facilities injecting CO2 for the long-
term containment in subsurface geologic formations would meet the
definition of GS in this proposed rule and would report additional
information. EPA is proposing that facilities that inject
CO2 for ER would not be GS facilities unless they inject
CO2 for the long-term containment in subsurface geologic
formations and submit and gain EPA approval of an MRV plan.
To comply with the specific reporting requirements discussed in
Section II.C of this preamble, the reporter would need to identify the
sources and surface equipment making up the GS facility. However, EPA
recognizes that defining the extent of a GS facility source may be
difficult. For example, there may be a number of injection wells in an
oilfield under common ownership or common control of which only a
subset would be considered GS facilities. In that example, the question
of whether and how to aggregate various wells arises. In addition, the
CO2 plume and pressure front associated with a GS facility
may extend for a distance beyond the injection point, and widely
separated wells may be injecting into the same pore space. Because EPA
is seeking data on the amount of CO2 sequestered by these
facilities and because EPA is proposing an all-in threshold for these
facilities, EPA is proposing a narrow definition of GS source to
simplify the reporting requirements associated with emissions from
combustion and surface equipment. For purposes of this reporting rule,
EPA is proposing to define a GS facility to include all structures
associated with the injection of CO2 located between the
points of CO2 transfer onsite from offsite and the injection
well (or wells). A GS facility that injects CO2 to enhance
the recovery of oil or natural gas will also include all structures
associated with production located between the production wells and the
separators.
Although EPA is proposing a narrow definition of GS facility, the
proposed rule would require GS facilities to monitor over a spatial
area that will almost certainly extend beyond the boundaries of the
facility, as defined here. Given that a main focus of this proposal is
to obtain information regarding the efficacy of GS, EPA anticipates
that the MRV plans for GS facilities will need to require monitoring
over a broad area. This is discussed in Section II.D of this preamble.
EPA seeks comment on its approach to defining the boundary of the
GS facility. In particular, EPA seeks comment on the question of
whether EPA should require the aggregation of wells located in an area,
and if so, what rules should be applied for determining what equipment
comprises the source. EPA seeks comment on whether the GS facility
should be defined to include the spatial area of monitoring proposed in
Section II.D of this preamble. EPA also seeks comment on whether it
should follow the approach for onshore facilities in the proposed
subpart W regulations, which requires the aggregation of equipment to
the geographic boundary of a single hydrocarbon basin as defined by the
American Association of Petroleum Geologists.
EPA is proposing to exempt research and development (R&D) as
defined at 40 CFR Part 98.6 from subpart RR, consistent with the
approach taken in subparts C through QQ of the MRR. EPA is also
proposing that, for the purposes of GS facility requirements under
subpart RR, research and development means those projects receiving
Federal funding to research practices and monitoring techniques that
will enable safe and effective long-term containment of a gaseous,
liquid, or supercritical CO2 stream in subsurface geologic
formations. R&D projects would not be required to submit an MRV plan
under subpart RR. EPA seeks comment on how R&D projects are defined and
treated in this proposal.
3. Other CO2 End-Users
In developing this proposed rule, EPA considered requiring
reporting from various other end-users of the CO2 that is
produced and supplied to the economy, including both emissive and
potentially non-emissive applications. EPA considered but is not
proposing requiring reporting from these other end-users; EPA has
concluded that collecting information pursuant to subpart PP on
CO2 supplied to the economy will provide EPA with the
necessary data on emissive volumes while minimizing the number of
facilities impacted by this rule. EPA seeks comment on this conclusion.
The Agency also seeks comment on whether applications, such as
precipitated calcium carbonate and some cement production, permanently
sequester CO2 and if so, which industries this would
include; how many facilities operate in
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each of these industries; how much of the CO2 consumed in
each industry would be sequestered; whether a sequestration factor
would be reasonable in any case; and what methodologies could be used
to verify this sequestration.
B. Selection of Reporting Thresholds
To determine the appropriate threshold for reporting under subpart
RR, EPA considered both a threshold based on the amount of
CO2 emitted and a threshold based on the amount of
CO2 injected underground. EPA concluded that an emissions-
based threshold would be problematic because of the lack of data on the
incidence and scale of surface emissions and leakage from injection and
GS of facilities. EPA seeks comment on how the Agency could determine
an emissions-based threshold and detailed data underlying such an
approach. EPA accordingly analyzed injection facilities based on the
quantity of CO2 injected underground and considered whether
an injection threshold should ap